US11400416B2 - Osmotic desalination methods and associated systems - Google Patents

Osmotic desalination methods and associated systems Download PDF

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US11400416B2
US11400416B2 US16/681,533 US201916681533A US11400416B2 US 11400416 B2 US11400416 B2 US 11400416B2 US 201916681533 A US201916681533 A US 201916681533A US 11400416 B2 US11400416 B2 US 11400416B2
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osmotic
osmotic membrane
draw
membrane
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Looh Tchuin Choong
Prakash Narayan Govindan
Maximus G. St. John
Steven Lam
Jonn-Ross Andrews
Karim M. Chehayeb
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Gradiant Corp
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    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D61/00Processes of separation using semi-permeable membranes, e.g. dialysis, osmosis or ultrafiltration; Apparatus, accessories or auxiliary operations specially adapted therefor
    • B01D61/58Multistep processes
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D61/00Processes of separation using semi-permeable membranes, e.g. dialysis, osmosis or ultrafiltration; Apparatus, accessories or auxiliary operations specially adapted therefor
    • B01D61/002Forward osmosis or direct osmosis
    • B01D61/0021Forward osmosis or direct osmosis comprising multiple forward osmosis steps
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D61/00Processes of separation using semi-permeable membranes, e.g. dialysis, osmosis or ultrafiltration; Apparatus, accessories or auxiliary operations specially adapted therefor
    • B01D61/002Forward osmosis or direct osmosis
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D61/00Processes of separation using semi-permeable membranes, e.g. dialysis, osmosis or ultrafiltration; Apparatus, accessories or auxiliary operations specially adapted therefor
    • B01D61/002Forward osmosis or direct osmosis
    • B01D61/0022Apparatus therefor
    • B01D61/022
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D61/00Processes of separation using semi-permeable membranes, e.g. dialysis, osmosis or ultrafiltration; Apparatus, accessories or auxiliary operations specially adapted therefor
    • B01D61/02Reverse osmosis; Hyperfiltration ; Nanofiltration
    • B01D61/025Reverse osmosis; Hyperfiltration
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D61/00Processes of separation using semi-permeable membranes, e.g. dialysis, osmosis or ultrafiltration; Apparatus, accessories or auxiliary operations specially adapted therefor
    • B01D61/02Reverse osmosis; Hyperfiltration ; Nanofiltration
    • B01D61/025Reverse osmosis; Hyperfiltration
    • B01D61/026Reverse osmosis; Hyperfiltration comprising multiple reverse osmosis steps
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F1/00Treatment of water, waste water, or sewage
    • C02F1/44Treatment of water, waste water, or sewage by dialysis, osmosis or reverse osmosis
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F1/00Treatment of water, waste water, or sewage
    • C02F1/44Treatment of water, waste water, or sewage by dialysis, osmosis or reverse osmosis
    • C02F1/441Treatment of water, waste water, or sewage by dialysis, osmosis or reverse osmosis by reverse osmosis
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F1/00Treatment of water, waste water, or sewage
    • C02F1/44Treatment of water, waste water, or sewage by dialysis, osmosis or reverse osmosis
    • C02F1/445Treatment of water, waste water, or sewage by dialysis, osmosis or reverse osmosis by forward osmosis
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D2311/00Details relating to membrane separation process operations and control
    • B01D2311/14Pressure control
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D2317/00Membrane module arrangements within a plant or an apparatus
    • B01D2317/02Elements in series
    • B01D2317/025Permeate series
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2103/00Nature of the water, waste water, sewage or sludge to be treated
    • C02F2103/08Seawater, e.g. for desalination
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2301/00General aspects of water treatment
    • C02F2301/08Multistage treatments, e.g. repetition of the same process step under different conditions
    • YGENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02ATECHNOLOGIES FOR ADAPTATION TO CLIMATE CHANGE
    • Y02A20/00Water conservation; Efficient water supply; Efficient water use
    • Y02A20/124Water desalination
    • Y02A20/131Reverse-osmosis

Definitions

  • Membranes which are selectively permeable to solvent (for example, water) and impermeable to dissolved ions (for example, Na + , Cl ⁇ ) have been used to desalinate aqueous feed solutions.
  • solvent for example, water
  • dissolved ions for example, Na + , Cl ⁇
  • membrane is transported from a feed solution through the semi-permeable membrane using a solution on the permeate side of the membrane that has an osmotic pressure that is higher than the osmotic pressure of the feed solution.
  • the driving force for separation in a forward osmosis process is the osmotic pressure gradient through the semi-permeable membrane; because the draw solution on one side of the membrane has a higher osmotic pressure than the feed solution on the other side of the membrane, water is drawn through the semi-permeable membrane from the feed solution to the draw solution to equalize the osmotic pressures of the feed and draw solutions.
  • reverse osmosis desalination Another type of membrane-based desalination is reverse osmosis desalination.
  • reverse osmosis processes use an applied hydraulic pressure as the driving force for separation.
  • the applied hydraulic pressure serves to counteract the osmotic pressure gradient that would otherwise favor water flux from low osmotic pressure to high osmotic pressure.
  • Membrane-based desalination systems have, to date, been limited by, for example, low efficiencies and have generally been limited to treating waters of relatively low salinities. Improved systems and methods for performing membrane-based desalination are desirable.
  • Certain embodiments are related to the use of a combination of forward osmosis and reverse osmosis to produce a stream comprising a relatively high water purity relative to the water purity of an aqueous feed stream.
  • the subject matter of the present invention involves, in some cases, interrelated products, alternative solutions to a particular problem, and/or a plurality of different uses of one or more systems and/or articles.
  • the method comprises transporting an aqueous feed stream containing a suspended and/or emulsified immiscible phase and solubilized ions at a concentration of at least about 60,000 ppm across a first side of a first osmotic membrane; and transporting a first draw inlet stream across a second side of the first osmotic membrane, the first draw inlet stream having a higher osmotic pressure than an osmotic pressure of the aqueous feed stream such that water is transported from the aqueous feed stream through the first osmotic membrane to the first draw inlet stream to produce a first draw product stream having a lower osmotic pressure than the first draw inlet stream and a concentrated aqueous stream having a higher concentration of solubilized ions than the aqueous feed stream.
  • Some such embodiments comprise directing the transport of the aqueous feed stream across the first osmotic membrane and/or the first draw inlet stream across the first osmotic membrane such that the following two ratios are within about 20% of each other: a ratio of a mass flow rate of the first draw inlet stream entering the first osmotic membrane to a mass flow rate of the aqueous feed stream entering the first osmotic membrane, and a ratio of the difference between the osmotic pressure of the aqueous feed stream entering the first osmotic membrane and the inlet pressure difference across the first osmotic membrane to the sum of the osmotic pressure of the first draw inlet stream entering the first osmotic membrane and the inlet pressure difference across the first osmotic membrane.
  • Some such embodiments comprise transporting at least a portion of the first draw product stream from the second side of the first osmotic membrane across a first side of a second osmotic membrane; transporting a second draw inlet stream across a second side of the second osmotic membrane; and applying a hydraulic pressure to the first side of the second osmotic membrane such that water is transported from the first draw product stream through the second osmotic membrane to the second draw inlet stream to produce a second draw product stream having a lower osmotic pressure than the second draw inlet stream and a second concentrated aqueous stream having a higher osmotic pressure than the first draw product stream.
  • Some such embodiments comprise directing the transport of the first draw product stream across the second osmotic membrane and/or the second draw inlet stream across the second osmotic membrane such that the following two ratios are within about 20% of each other: a ratio of a mass flow rate of the second draw inlet stream entering the second osmotic membrane to a mass flow rate of the first draw product stream entering the second osmotic membrane, and a ratio of the difference between the osmotic pressure of the first draw product stream entering the second osmotic membrane and the inlet pressure difference across the second osmotic membrane to the sum of the osmotic pressure of the second draw inlet stream entering the second osmotic membrane and the inlet pressure difference across the second osmotic membrane.
  • Certain embodiments comprise transporting an aqueous feed stream containing a suspended and/or emulsified immiscible phase and solubilized ions at a concentration of at least about 60,000 ppm across a first side of a first osmotic membrane; and transporting a first draw inlet stream across a second side of the first osmotic membrane, the first draw inlet stream having a higher osmotic pressure than an osmotic pressure of the aqueous feed stream such that water is transported from the aqueous feed stream through the first osmotic membrane to the first draw inlet stream to produce a first draw product stream having a lower osmotic pressure than the first draw inlet stream and a concentrated aqueous stream having a higher concentration of solubilized ions than the aqueous feed stream.
  • Some such embodiments comprise directing the transport of the aqueous feed stream across the first osmotic membrane and/or the first draw inlet stream across the first osmotic membrane such that the transmembrane net driving force at the entrance of the aqueous feed stream to the first osmotic membrane and the transmembrane net driving force at the entrance of the first draw inlet stream to the first osmotic membrane are within about 10% of each other.
  • Some such embodiments comprise transporting at least a portion of the first draw product stream from the second side of the first osmotic membrane across a first side of a second osmotic membrane; transporting a second draw inlet stream across a second side of the second osmotic membrane.
  • Some such embodiments comprise applying a hydraulic pressure to the first side of the second osmotic membrane such that water is transported from the first draw product stream through the second osmotic membrane to the second draw inlet stream to produce a second draw product stream having a lower osmotic pressure than the second draw inlet stream and a second concentrated aqueous stream having a higher osmotic pressure than the first draw product stream; and directing the transport of the first draw product stream across the second osmotic membrane and/or the second draw inlet stream across the second osmotic membrane such that the transmembrane net driving force at the entrance of the first draw product stream to the second osmotic membrane and the transmembrane net driving force at the entrance of the second draw inlet stream across the second osmotic membrane are within about 10% of the each other.
  • the method comprises transporting an aqueous feed stream containing a suspended and/or emulsified immiscible phase and solubilized ions at a concentration of at least about 60,000 ppm across a first side of a first osmotic membrane; transporting a first draw inlet stream across a second side of the first osmotic membrane, the first draw inlet stream having a higher osmotic pressure than an osmotic pressure of the aqueous feed stream such that water is transported from the aqueous feed stream through the first osmotic membrane to the first draw inlet stream to produce a first draw product stream having a lower osmotic pressure than the first draw inlet stream and a concentrated aqueous stream having a higher concentration of solubilized ions than the aqueous feed stream; and directing the transport of the aqueous feed stream across the first osmotic membrane and/or the first draw inlet stream across the first osmotic membrane such that
  • Some such embodiments comprise measuring at least one of a temperature, a pressure, a solubilized species concentration, and a flow rate of the aqueous feed stream and/or the first draw inlet stream; and changing at least one of the flow rate of the aqueous feed stream and the flow rate of the first draw inlet stream such that the transmembrane net driving force at the entrance of the aqueous feed stream to the first osmotic membrane and the transmembrane net driving force at the entrance of the first draw inlet stream to the first osmotic membrane are within about 10% of each other.
  • Some such embodiments comprise transporting at least a portion of the first draw product stream from the second side of the first osmotic membrane across a first side of a second osmotic membrane; transporting a second draw inlet stream across a second side of the second osmotic membrane; applying a hydraulic pressure to the first side of the second osmotic membrane such that water is transported from the first draw product stream through the second osmotic membrane to the second draw inlet stream to produce a second draw product stream having a lower osmotic pressure than the second draw inlet stream and a second concentrated aqueous stream having a higher osmotic pressure than the first draw product stream; and directing the transport of the first draw product stream across the second osmotic membrane and/or the second draw inlet stream across the second osmotic membrane such that the transmembrane net driving force at the entrance of the first draw product stream to the second osmotic membrane and the transmembrane net driving force at the entrance of the second draw inlet
  • Some such embodiments comprise measuring at least one of a temperature, a pressure, a solubilized species concentration, and a flow rate of the first draw product stream and/or the second draw inlet stream; and changing at least one of the flow rate of the first draw product stream and the flow rate of the second draw inlet stream such that the transmembrane net driving force at the entrance of the first draw product stream to the second osmotic membrane and the transmembrane net driving force at the entrance of the second draw inlet stream to the second osmotic membrane are within about 10% of each other.
  • the method comprises transporting an aqueous feed stream containing a suspended and/or emulsified immiscible phase and solubilized ions at a concentration of at least about 60,000 ppm across a first side of a first osmotic membrane; transporting a first draw inlet stream across a second side of the first osmotic membrane, the first draw inlet stream having a higher osmotic pressure than an osmotic pressure of the aqueous feed stream such that water is transported from the aqueous feed stream through the first osmotic membrane to the first draw inlet stream to produce a first draw product stream having a lower osmotic pressure than the first draw inlet stream and a concentrated aqueous stream having a higher concentration of solubilized ions than the aqueous feed stream; transporting at least a portion of the first draw product stream from the second side of the first osmotic membrane across a first side of a second osmotic membrane;
  • m D ⁇ ⁇ 1 , i m F ⁇ ⁇ 1 , i C 1 ⁇ ⁇ F ⁇ ⁇ 1 , i - ( P F ⁇ ⁇ 1 - P D ⁇ ⁇ 1 ) ⁇ D ⁇ ⁇ 1 , i + ( P F ⁇ ⁇ 1 - P D ⁇ ⁇ 1 )
  • P F1 is a hydraulic pressure at an inlet of the aqueous feed stream to the first osmotic membrane
  • m F1,i is a mass flow rate of the aqueous feed stream at the inlet of the aqueous feed stream to the first osmotic membrane
  • ⁇ F1,i is an osmotic pressure of the aqueous feed stream at the inlet of the aqueous feed stream to the first osmotic membrane
  • P D1 is a hydraulic pressure at an inlet of the first draw inlet stream to the first osmotic membrane
  • m D1,i is a mass flow rate of
  • m D ⁇ ⁇ 2 , i m F ⁇ ⁇ 2 , i C 2 ⁇ ⁇ F ⁇ ⁇ 2 , i - ( P F ⁇ ⁇ 2 - P D ⁇ ⁇ 2 ) ⁇ D ⁇ ⁇ 2 , i + ( P F ⁇ ⁇ 2 - P D ⁇ ⁇ 2 )
  • P F2 is a hydraulic pressure at an inlet of the first draw product stream to the second osmotic membrane
  • m F2,i is a mass flow rate of the first draw product stream at the inlet of the first draw product stream to the second osmotic membrane
  • ⁇ F2,i is an osmotic pressure of the first draw product stream at the inlet of the first draw product stream to the second osmotic membrane
  • P D2 is a hydraulic pressure at an inlet of the second draw inlet stream to the second osmotic membrane
  • m D2,i is a mass flow rate of the second draw inlet stream at the inlet
  • the method comprises transporting an aqueous feed stream containing solubilized ions across a first side of a first osmotic membrane; transporting a first draw inlet stream across a second side of the first osmotic membrane, the first draw inlet stream having a higher osmotic pressure than an osmotic pressure of the aqueous feed stream such that water is transported from the aqueous feed stream through the first osmotic membrane to the first draw inlet stream to produce a first draw product stream having a lower osmotic pressure than the first draw inlet stream and a concentrated aqueous stream having a higher concentration of solubilized ions than the aqueous feed stream; transporting at least a portion of the first draw product stream from the second side of the first osmotic membrane across a first side of a second osmotic membrane; transporting a second draw inlet stream across a second side of the second osmotic membrane; and applying a hydraulic pressure to the
  • the method comprises, according to certain embodiments, transporting an aqueous feed stream across a first side of an osmotic membrane; and transporting a draw inlet stream across a second side of the osmotic membrane such that water is transported from the aqueous feed stream through the osmotic membrane to the draw inlet stream to produce a draw product stream having a lower osmotic pressure than the draw inlet stream and a concentrated aqueous stream having a higher osmotic pressure than the aqueous feed stream; wherein the osmotic membrane is operated such that:
  • m D , i m F , i C 1 ⁇ ⁇ F , i - ( P F - P D ) ⁇ D , i + ( P F - P D )
  • P F is a hydraulic pressure at an inlet of the aqueous feed stream to the osmotic membrane
  • m F,i is a mass flow rate of the aqueous feed stream at the inlet of the aqueous feed stream to the osmotic membrane
  • ⁇ F1,i is an osmotic pressure of the aqueous feed stream at the inlet of the aqueous feed stream to the osmotic membrane
  • P D is a hydraulic pressure at an inlet of the draw inlet stream to the osmotic membrane
  • m D,i is a mass flow rate of the draw inlet stream at the inlet of the draw inlet stream to the osmotic membrane
  • ⁇ D,i is an osmotic pressure of the draw inlet stream at the in
  • the method comprises transporting an aqueous feed stream across a first side of an osmotic membrane; transporting a draw inlet stream across a second side of the osmotic membrane such that water is transported from the aqueous feed stream through the osmotic membrane to the draw inlet stream to produce a draw product stream having a lower osmotic pressure than the draw inlet stream and a concentrated aqueous stream having a higher osmotic pressure than the aqueous feed stream; and directing the transport of the aqueous feed stream across the osmotic membrane and/or the draw inlet stream across the osmotic membrane such that the following two ratios are within about 20% of each other: a ratio of a mass flow rate of the draw inlet stream entering the osmotic membrane to a mass flow rate of the aqueous feed stream entering the osmotic membrane, and a ratio of the difference between the osmotic pressure of the aqueous feed stream entering the
  • the method comprises, according to some embodiments, transporting an aqueous feed stream across a first side of an osmotic membrane; transporting a draw inlet stream across a second side of the osmotic membrane such that water is transported from the aqueous feed stream through the osmotic membrane to the draw inlet stream to produce a draw product stream having a lower osmotic pressure than the draw inlet stream and a concentrated aqueous stream having a higher osmotic pressure than the aqueous feed stream; and directing the transport of the aqueous feed stream across the osmotic membrane and/or the draw inlet stream across the osmotic membrane such that the transmembrane net driving force at the entrance of the aqueous feed stream to the osmotic membrane and the transmembrane net driving force at the entrance of the draw inlet stream to the osmotic membrane are within about 10% of each other.
  • the method comprises, according to certain embodiments, transporting an aqueous feed stream across a first side of an osmotic membrane; transporting a draw inlet stream across a second side of the osmotic membrane such that water is transported from the aqueous feed stream through the osmotic membrane to the draw inlet stream to produce a draw product stream having a lower osmotic pressure than the draw inlet stream and a concentrated aqueous stream having a higher osmotic pressure than the aqueous feed stream; directing the transport of the aqueous feed stream across the osmotic membrane and/or the draw inlet stream across the osmotic membrane such that the transmembrane net driving force at the entrance of the aqueous feed stream to the osmotic membrane and the transmembrane net driving force at the entrance of the draw inlet stream to the osmotic membrane are at least about 10% different from each other; measuring at least one of a temperature, a pressure, a solubilized
  • FIG. 1A is a schematic illustration of an osmotic membrane separator, according to certain embodiments.
  • FIG. 1B is a cross-sectional illustration of the osmotic membrane separator shown in FIG. 1A ;
  • FIG. 1C is a front, top, right side perspective view of an osmotic membrane, according to some embodiments.
  • FIG. 1D is a front, bottom, right side perspective view of the exemplary osmotic membrane illustrated in FIG. 1C ;
  • FIG. 2A is a schematic illustration of an exemplary osmotic desalination system, according to certain embodiments.
  • FIG. 2B is, according to some embodiments, a schematic illustration of an osmotic desalination system
  • FIG. 3A is a schematic illustration of an exemplary osmotic desalination system comprising a forward osmosis separator coupled with a series of reverse osmosis separators, according to certain embodiments;
  • FIG. 3B is, according to some embodiments, a schematic illustration of an exemplary osmotic desalination system comprising a forward osmosis separator coupled with a series of reverse osmosis separator and including energy recovery apparatuses;
  • FIG. 4A is a schematic diagram illustrating the operation of an osmotic separator, according to one set of embodiments.
  • FIG. 4B is an exemplary plot of osmotic pressure as a function of position across an osmotic membrane, according to one embodiment.
  • multiple osmotic membrane separators may be used to perform a series of osmosis steps, such that an output stream having a relatively high water purity—compared to a water purity of an aqueous feed stream—is produced.
  • multiple draw streams can be used to produce aqueous product streams having sequentially higher purities of water.
  • Certain embodiments are related to osmotic desalination systems and methods in which forward osmosis is used to produce a first product stream having a relatively high water purity relative to an aqueous feed stream, and reverse osmosis is used to perform a second step (and/or additional steps) on the first product stream.
  • the use of reverse osmosis in subsequent, downstream steps can also allow one to take advantage of the low energy consumption of reverse osmosis relative to, for example, thermal desalination processes such as thermal evaporation/distillation.
  • Employing combinations of forward and reverse osmosis steps in this way can, according to certain embodiments, produce a low-energy, low-fouling desalination system that produces a product stream with a high water purity (and low salinity) relative to an aqueous feed stream.
  • multiple reverse osmosis steps can be used in series as part of a system to perform net desalination (i.e., to produce a product stream having a relatively high purity of water compared to the purity of water in an inlet aqueous stream).
  • net desalination i.e., to produce a product stream having a relatively high purity of water compared to the purity of water in an inlet aqueous stream.
  • steps can be performed, each achieving a relatively small increase in purity to produce a final product that contains a higher purity of water than the aqueous feed stream.
  • Such arrangements may be useful, for example, when desalinating aqueous feed streams with very high osmotic pressures (e.g., osmotic pressures of 60 bar, or greater).
  • Certain embodiments relate to systems and methods in which strategies are employed to reduce energy consumption in osmotic desalination systems.
  • the osmotic desalination membrane(s) can be operated such that the transmembrane net driving force (i.e., the net driving force through the thickness of the membrane) is relatively uniform across the facial area of the membrane(s). Such uniformity may, according to certain embodiments, reduce or eliminate unnecessary over-pressurization along the osmotic membrane, which can in turn reduce or eliminate wasted energy during operation of the system.
  • aqueous feed streams can be used to treat a wide variety of aqueous feed streams, including but not limited to streams derived from seawater, ground water, brackish water, and/or the effluent of a chemical process.
  • the aqueous feed stream contains a relatively large amount of solubilized ions, for example, at a concentration of at least about 60,000 ppm.
  • the aqueous feed contains, in addition to ions solubilized in water, a suspended and/or emulsified phase that is immiscible in water (e.g., oil and/or grease).
  • FIG. 1A is an exemplary schematic diagram illustrating the use of an osmotic membrane separator to desalinate an aqueous feed stream.
  • FIG. 1B is a cross-sectional illustration of the schematic shown in FIG. 1A .
  • osmotic membrane 102 can be used to transport water from first side 104 to second side 106 . In some cases, this may result in at least partial separation of water within aqueous feed stream 108 from solubilized ions (or other solubilized species) within aqueous feed stream 108 .
  • Aqueous feed stream 108 can be transported across first side 104 of osmotic membrane 102 , for example, in the direction of arrow 103 in FIG. 1B .
  • Draw inlet stream 110 can, in some embodiments, be transported across second side 106 of osmotic membrane 102 , for example, in the direction of arrow 105 in FIG. 1B .
  • Transport of water through the osmotic membrane can be achieved via a transmembrane net driving force (i.e., a net driving force through the thickness of the membrane), according to certain embodiments.
  • P 1 ⁇ P 2 can be referred to as the transmembrane hydraulic pressure gradient, and ( ⁇ 1 ⁇ 2 ) can be referred to
  • osmotic pressure of a particular liquid is an intrinsic property of the liquid.
  • the osmotic pressure can be determined in a number of ways, with the most efficient method depending upon the type of liquid being analyzed. For certain solutions with relatively low molar concentrations of ions, osmotic pressure can be accurately measured using an osmometer. In other cases, the osmotic pressure can simply be determined by comparison with solutions with known osmotic pressures.
  • osmotic pressure of an uncharacterized solution one could apply a known amount of the uncharacterized solution on one side of a non-porous, semi-permeable, osmotic membrane and iteratively apply different solutions with known osmotic pressures on the other side of the osmotic membrane until the differential pressure through the thickness of the membrane is zero.
  • Forward osmosis generally occurs when the osmotic pressure on the second (permeate) side of the osmotic membrane is greater than the osmotic pressure on the first (retentate) side of the osmotic membrane such that water is transported from the first side of the osmotic membrane to the second side of the osmotic membrane.
  • water In forward osmosis systems, water generally is transported from the first side of the osmotic membrane to the second side of the osmotic membrane as long as the hydraulic pressure difference between the second side of the osmotic membrane and the first side of the osmotic membrane is not sufficiently high to overcome the osmotic pressure difference between the first and second sides of the osmotic membrane. In this way, the permeate flow and the osmotic driving force are aligned in the same direction.
  • the stream on the second side of the osmotic membrane can initiate the transport of water from the stream of the first side of the osmotic membrane through the osmotic membrane from the first side to the second side, resulting in the production of a stream having a higher osmotic pressure (e.g., more concentrated in solubilized species (e.g., dissolved ions and/or disassociated molecules)) relative to the aqueous feed stream.
  • a higher osmotic pressure e.g., more concentrated in solubilized species (e.g., dissolved ions and/or disassociated molecules)
  • osmotic membrane 102 can be used to perform forward osmosis, for example, when the osmotic pressure on second side 106 is higher than the osmotic pressure on first side 104 , and the hydraulic pressure gradient from second side 106 to first side 104 (P 106 ⁇ P 104 ) is not large enough to overcome the difference in the osmotic pressures on first side 104 and second side 106 . In such cases, water can be transported from first side 104 of osmotic membrane 102 to second side 106 of osmotic membrane 102 .
  • stream 114 which can have a higher osmotic pressure than the osmotic pressure of stream 108 .
  • stream 108 contains solubilized species (e.g., ions)
  • the forward osmosis process can result in the production of concentrated aqueous stream 114 , which can contain solubilized species (e.g., ions) at a molar concentration greater than the molar concentration of solubilized species (e.g., ions) in stream 108 .
  • the forward osmosis process can result, according to some embodiments, in the production of draw product stream 112 , which can have a lower osmotic pressure than the osmotic pressure of stream 110 .
  • the draw product stream 112 can contain the solubilized species (e.g., ions) at a lower molar concentration than the molar concentration of solubilized species (e.g., ions) within stream 110 .
  • pressure may be applied to enhance the forward osmosis process.
  • pressure may be applied to the first side of the osmotic membrane such that the hydraulic pressure of the stream on the first side of the osmotic membrane is higher than the hydraulic pressure of the stream on the second side of the osmotic membrane.
  • the applied pressure can increase the rate at which water is transported from the first side of the osmotic membrane to the second side of the osmotic membrane.
  • Such arrangements are sometimes referred to herein as pressure-assisted forward osmosis.
  • forward osmosis is performed in the substantial absence of an applied pressure (e.g., such that the hydraulic pressure gradient through the osmotic membrane is less than or equal to about 0.1 bar).
  • Osmotic membranes can be used, according to certain embodiments, to perform reverse osmosis.
  • Reverse osmosis generally occurs when the osmotic pressure on the first (retentate) side of the osmotic membrane is greater than the osmotic pressure on the second (permeate) side of the osmotic membrane, and a pressure is applied to the first side of the osmotic membrane such that the hydraulic pressure on the first side of the osmotic membrane is sufficiently greater than the hydraulic pressure on the second side of the osmotic membrane to cause water to be transported from the first side of the osmotic membrane to the second side of the osmotic membrane.
  • osmotic membrane 102 can be used to perform reverse osmosis, for example, when the osmotic pressure on first side 104 is higher than the osmotic pressure on second side 106 , a pressure is applied to first side such that the hydraulic pressure on first side 104 is higher than the hydraulic pressure on second side 106 , and the difference between the hydraulic pressure on first side 104 and the hydraulic pressure on second side 106 is greater than the difference between the osmotic pressure on side 104 and the osmotic pressure on side 106 . In such cases, water can be transported from first side 104 of osmotic membrane 102 to second side 106 of osmotic membrane 102 .
  • stream 114 which can have a higher osmotic pressure than stream 108 .
  • solubilized species e.g., ions
  • the reverse osmosis process can result, according to certain embodiments, in the production of concentrated aqueous stream 114 , which can contain solubilized species (e.g., ions) at a molar concentration greater than the molar concentration of solubilized species (e.g., ions) in stream 108 .
  • draw product stream 112 which can have a lower osmotic pressure than the osmotic pressure of stream 110 .
  • solubilized species e.g., ions
  • the reverse osmosis process can result in the production of draw product stream 112 , which can contain solubilized species (e.g., ions) at a lower molar concentration than the molar concentration of solubilized species (e.g., ions) within stream 110 .
  • FIG. 2A is a schematic illustration of an exemplary desalination system 200 , according to certain embodiments.
  • desalination system 200 comprises first osmotic membrane 202 , which has first side 204 and second side 206 .
  • Desalination system 200 also comprises second osmotic membrane 216 , which has first side 218 and second side 220 .
  • the first osmotic membrane can be used to perform a first osmosis step
  • the second osmotic membrane can be used to perform a second osmosis step.
  • first osmotic membrane 202 can be used to perform a first osmosis step (e.g., a forward osmosis step), and second osmotic membrane 216 can be used to perform a second osmosis step (e.g., a reverse osmosis step).
  • first osmosis step e.g., a forward osmosis step
  • second osmotic membrane 216 can be used to perform a second osmosis step (e.g., a reverse osmosis step).
  • Certain embodiments comprise transporting an aqueous feed stream containing solubilized ions across a first side of a first osmotic membrane.
  • aqueous feed stream 208 containing solubilized ions can be transported across first side 204 of first osmotic membrane 202 .
  • Some embodiments comprise transporting a first draw inlet stream across a second side of the first osmotic membrane.
  • first draw inlet stream 210 can be transported across second side 206 of first osmotic membrane 202 .
  • the first draw inlet stream has a higher osmotic pressure than the osmotic pressure of the aqueous feed stream (e.g., due to a higher molar concentration of total solubilized species within the first draw inlet stream than in the aqueous feed stream).
  • the osmotic pressure of the first draw inlet stream is higher than the osmotic pressure of the aqueous feed stream such that water is transported from the aqueous feed stream through the first osmotic membrane to the first draw inlet stream.
  • this process can produce a first draw product stream having a lower osmotic pressure than the first draw inlet stream (e.g., due to a lower molar concentration of solubilized species in the first draw product stream than in the first draw inlet stream).
  • the process can also produce a concentrated aqueous stream having a higher molar concentration of solubilized ions than the aqueous feed stream.
  • first draw inlet stream 210 can, in some embodiments, have an osmotic pressure that is sufficiently high such that water is transported from aqueous feed stream 208 through first osmotic membrane 202 to first draw inlet stream 210 .
  • Transport of water through osmotic membrane 202 can result in the production of first draw product stream 212 having a lower osmotic pressure than first draw inlet stream 210 (e.g., due to a lower molar concentration of solubilized species (e.g., ions) within draw product stream 212 than in draw inlet stream 210 ).
  • Transport of water through osmotic membrane 202 can also result in the production of concentrated aqueous stream 214 having a higher molar concentration of solubilized ions than aqueous feed stream 208 .
  • the concentrated aqueous stream (e.g., 214 in FIGS. 2A-2B ) can have an osmotic pressure that is at least about 1.01 times, at least about 1.1 times, at least about 1.5 times, at least about 2 times, at least about 5 times, at least about 10 times, or at least about 50 times (and/or, in some embodiments, up to about 100 times, up to about 500 times, up to about 1000 times, up to about 5000 times, or more) the osmotic pressure of the aqueous feed stream (e.g., stream 208 in FIGS. 2A-2B ).
  • the concentrated aqueous stream (e.g., 214 in FIGS. 2A-2B ) can have a weight percentage of solubilized species (e.g., ions) that is at least about 1.01 times, at least about 1.1 times, at least about 1.5 times, at least about 2 times, at least about 5 times, at least about 10 times, or at least about 50 times (and/or, in some embodiments, up to about 100 times, up to about 500 times, up to about 1000 times, up to about 5000 times, or more) the weight percentage of solubilized species (e.g., ions) in the aqueous feed stream (e.g., stream 208 in FIGS. 2A-2B ).
  • solubilized species e.g., ions
  • first aqueous feed stream 208 can have a solubilized ion concentration of 10 wt % and first concentrated aqueous stream 214 can have a solubilized ion concentration of 20 wt %, which is 2 times the weight percentage of solubilized ions in the first aqueous feed stream.
  • the first draw inlet stream (e.g., stream 210 in FIGS. 2A-2B ) can have an osmotic pressure that is at least about 1.01 times, at least about 1.1 times, at least about 1.5 times, at least about 2 times, at least about 5 times, at least about 10 times, or at least about 50 times (and/or, in some embodiments, up to about 100 times, up to about 500 times, up to about 1000 times, up to about 5000 times, or more) the osmotic pressure of the first draw product stream (e.g., stream 212 in FIGS. 2A-2B ).
  • the first draw inlet stream (e.g., stream 210 in FIGS. 2A-2B ) can have a weight percentage of solubilized species (e.g., ions) that is at least about 1.01 times, at least about 1.1 times, at least about 1.5 times, at least about 2 times, at least about 5 times, at least about 10 times, or at least about 50 times (and/or, in some embodiments, up to about 100 times, up to about 500 times, up to about 1000 times, up to about 5000 times, or more) the weight percentage of solubilized ions in the first draw product stream (e.g., stream 212 in FIGS. 2A-2B ).
  • solubilized species e.g., ions
  • first draw product stream 212 can have a solubilized ion concentration of 12 wt % and first draw inlet stream 210 can have a solubilized ion concentration of 20 wt %, which is 1.67 times the weight percentage of solubilized ions in the first draw product stream.
  • the first osmotic membrane separator can be operated as a forward osmosis membrane separator.
  • the osmotic pressure of the stream on the first side of the first osmotic membrane can be lower than the osmotic pressure of the stream on the second side of the first osmotic membrane such that water is transported from the first side of the first osmotic membrane to the second side of the first osmotic membrane, at least in part, due to the transmembrane osmotic pressure difference.
  • the forward osmosis process can be carried out in the substantial absence of an applied hydraulic pressure on the first side of the osmotic membrane. For example, referring to FIG.
  • forward osmosis can be performed using osmotic membrane 202 (e.g., as described above) in the substantial absence of a hydraulic pressure applied to the liquid on first side 204 of osmotic membrane 202 .
  • the forward osmosis process can be a pressure-assisted forward osmosis process, in which a substantial hydraulic pressure is applied to the first side of the osmotic membrane.
  • forward osmosis can be performed using osmotic membrane 202 (e.g., as described above) while a hydraulic pressure is applied to the liquid on first side 204 of osmotic membrane 202 .
  • Certain embodiments comprise transporting at least a portion of the first draw product stream from the second side of the first osmotic membrane across a first side of a second osmotic membrane.
  • first draw product stream 212 can be transported across first side 218 of the second osmotic membrane 216 .
  • Some embodiments comprise transporting a second draw inlet stream across a second side of the second osmotic membrane.
  • second draw inlet stream 222 can be transported across second side 220 of second osmotic membrane 216 .
  • Certain embodiments comprise applying a hydraulic pressure to the first side of the second osmotic membrane such that water is transported from the first draw product stream through the second osmotic membrane to the second draw inlet stream to produce a second draw product stream having a lower osmotic pressure (e.g., due to a lower molar concentration of solubilized species (e.g., ions)) than the second draw inlet stream and a second concentrated aqueous stream having a higher osmotic pressure (e.g., due to a higher molar concentration of solubilized species (e.g., ions)) than the first draw product stream.
  • a hydraulic pressure to the first side of the second osmotic membrane such that water is transported from the first draw product stream through the second osmotic membrane to the second draw inlet stream to produce a second draw product stream having a lower osmotic pressure (e.g., due to a lower molar concentration of solubilized species (e.g.,
  • a hydraulic pressure is applied to first side 218 of second osmotic membrane 216 such that water is transported from first draw product stream 212 through second osmotic membrane 216 to second draw inlet stream 222 to produce second draw product stream 224 having a lower osmotic pressure (e.g., due to a lower molar concentration of solubilized species (e.g., ions)) than second draw inlet stream 222 and second concentrated aqueous stream 226 having a higher osmotic pressure (e.g., due to a higher molar concentration of solubilized species (e.g., ions)) than first draw product stream 212 .
  • a lower osmotic pressure e.g., due to a lower molar concentration of solubilized species (e.g., ions)
  • second concentrated aqueous stream 226 having a higher osmotic pressure (e.g., due to a higher molar concentration of solubilized species (e.
  • the second concentrated aqueous stream (e.g., 226 in FIGS. 2A-2B ) can have an osmotic pressure that is at least about 1.01 times, at least about 1.1 times, at least about 1.5 times, at least about 2 times, at least about 5 times, at least about 10 times, or at least about 50 times (and/or, in some embodiments, up to about 100 times, up to about 500 times, up to about 1000 times, up to about 5000 times, or more) the osmotic pressure of the first draw product stream (e.g., stream 212 in FIGS. 2A-2B ).
  • the second concentrated aqueous stream (e.g., 226 in FIGS. 2A-2B ) can have a weight percentage of solubilized species (e.g., ions) that is at least about 1.01 times, at least about 1.1 times, at least about 1.5 times, at least about 2 times, at least about 5 times, at least about 10 times, or at least about 50 times (and/or, in some embodiments, up to about 100 times, up to about 500 times, up to about 1000 times, up to about 5000 times, or more) the weight percentage of solubilized species (e.g., ions) in the first draw product stream (e.g., stream 212 in FIGS. 2A-2B ).
  • a weight percentage of solubilized species e.g., ions
  • first draw product stream 212 can have a solubilized ion concentration of 12 wt % and second concentrated aqueous stream 226 can have a solubilized ion concentration of 22 wt %, which is 1.83 times the weight percentage of solubilized ions in the first draw product stream.
  • the second draw inlet stream (e.g., stream 222 in FIGS. 2A-2B ) can have an osmotic pressure that is at least about 1.01 times, at least about 1.1 times, at least about 1.5 times, at least about 2 times, at least about 5 times, at least about 10 times, or at least about 50 times (and/or, in some embodiments, up to about 100 times, up to about 500 times, up to about 1000 times, up to about 5000 times, or more) the osmotic pressure of the second draw product stream (e.g., stream 224 in FIGS. 2A-2B ).
  • the second draw inlet stream (e.g., stream 222 in FIGS. 2A-2B ) can have a weight percentage of solubilized species (e.g., ions) that is at least about 1.01 times, at least about 1.1 times, at least about 1.5 times, at least about 2 times, at least about 5 times, at least about 10 times, or at least about 50 times (and/or, in some embodiments, up to about 100 times, up to about 500 times, up to about 1000 times, up to about 5000 times, or more) the weight percentage of solubilized species (e.g., ions) in the second draw product stream (e.g., stream 224 in FIGS. 2A-2B ).
  • solubilized species e.g., ions
  • second draw product stream 224 can have a solubilized ion concentration of 10 wt % and second draw inlet stream 222 can have a solubilized ion concentration of 20 wt %, which is 2 times the weight percentage of solubilized ions in the second draw product stream.
  • the second osmotic membrane separator can be operated as a reverse osmosis membrane separator, according to certain embodiments. That is to say, in some embodiments, water can be transported from the first side of the second osmotic membrane to the second side of the second osmotic membrane by applying a hydraulic pressure to the first side of the second osmotic membrane as a driving force, such that local osmotic pressure gradients through the thickness of the membrane that would otherwise favor the transport of water from the second side of the membrane to the first side of the membrane are overcome by the applied hydraulic pressure.
  • the osmotic pressure of the stream on the first side of the second osmotic membrane can be higher than the osmotic pressure of the stream on the second side of the second osmotic membrane, such that water is transported through the second osmotic membrane due to a hydraulic pressure applied to the first side of the second osmotic membrane.
  • FIG. 2B is a schematic illustration of an exemplary desalination system 260 , according to certain embodiments.
  • desalination system 260 comprises first osmotic membrane 202 (which comprises first side 204 and second side 206 ) and second osmotic membrane 216 (which comprises first side 218 and second side 220 ).
  • first osmotic membrane 202 and second osmotic membrane 216 can be operated as described elsewhere herein with respect to membranes 202 and 216 (e.g., as shown in FIG. 2A ).
  • System 2B further comprises a third osmotic membrane 228 , comprising first side 230 and second side 232 .
  • System 260 also comprises optional fourth osmotic membrane 240 , comprising first side 242 and second side 244 .
  • the first osmotic membrane can be used to perform a first osmosis step
  • the second osmotic membrane can be used to perform a second osmosis step
  • the third osmotic membrane can be used to perform a third osmosis step.
  • the fourth osmotic membrane when present, can be used to perform a fourth osmosis step, according to certain embodiments.
  • first osmotic membrane 202 can be used to perform a first osmosis step (e.g., a forward osmosis desalination step), second osmotic membrane 216 can be used to perform a second osmosis step (e.g., a first reverse osmosis desalination step), and third osmotic membrane 228 can be used to perform a third osmosis step (e.g., a second reverse osmosis desalination step).
  • optional fourth osmotic membrane can be used to perform a fourth osmosis step (e.g., a third reverse osmosis step).
  • first osmotic membrane 202 and second osmotic membrane 216 can be operated as described elsewhere. Some embodiments comprise transporting at least a portion of the second draw product stream from the second side of the second osmotic membrane across a first side of a third osmotic membrane. For example, referring to FIG. 2B , in some embodiments, at least a portion of second draw product stream 224 is transported from the second side 220 of the second osmotic membrane 216 across first side 230 of third osmotic membrane 228 . Certain embodiments comprise transporting a third draw inlet stream across a second side of the third osmotic membrane. For example, referring to FIG. 2B , in some embodiments, third draw inlet stream 234 is transported across second side 232 of third osmotic membrane 228 .
  • Some embodiments comprise applying a hydraulic pressure to the second draw product stream on the first side of the third osmotic membrane such that water is transported from the second draw product stream through the third osmotic membrane to the third draw inlet stream to produce a third draw product stream having a lower osmotic pressure (e.g., due to a lower molar concentration of solubilized species (e.g., ions)) than the third draw inlet stream and a third concentrated stream having a higher osmotic pressure (e.g., due to a higher molar concentration of solubilized species (e.g., ions)) than the second draw product stream.
  • a hydraulic pressure to the second draw product stream on the first side of the third osmotic membrane such that water is transported from the second draw product stream through the third osmotic membrane to the third draw inlet stream to produce a third draw product stream having a lower osmotic pressure (e.g., due to a lower molar concentration of solubil
  • a hydraulic pressure is applied to second draw product stream 224 on first side 230 of third osmotic membrane 228 such that water is transported from second draw product stream 224 through third osmotic membrane 228 to third draw inlet stream 234 to produce third draw product stream 236 having a lower osmotic pressure (e.g., due to a lower molar concentration of solubilized species (e.g., ions)) than third draw inlet stream 234 and third concentrated aqueous stream 238 having a higher osmotic pressure (e.g., due to a higher molar concentration of solubilized species (e.g., ions)) than second draw product stream 224 .
  • a lower osmotic pressure e.g., due to a lower molar concentration of solubilized species (e.g., ions)
  • third draw inlet stream 234 e.g., due to a lower molar concentration of solubilized species (e.g., ions
  • the third concentrated aqueous stream (e.g., 238 in FIG. 2B ) can have an osmotic pressure that is at least about 1.01 times, at least about 1.1 times, at least about 1.5 times, at least about 2 times, at least about 5 times, at least about 10 times, or at least about 50 times (and/or, in some embodiments, up to about 100 times, up to about 500 times, up to about 1000 times, up to about 5000 times, or more) the osmotic pressure of the second draw product stream (e.g., stream 224 in FIG. 2B ).
  • the third concentrated aqueous stream (e.g., 238 in FIG. 2B ) can have a weight percentage of solubilized species (e.g., ions) that is at least about 1.01 times, at least about 1.1 times, at least about 1.5 times, at least about 2 times, at least about 5 times, at least about 10 times, or at least about 50 times (and/or, in some embodiments, up to about 100 times, up to about 500 times, up to about 1000 times, up to about 5000 times, or more) the weight percentage of solubilized species (e.g., ions) in the second draw product stream (e.g., stream 224 in FIG. 2B ).
  • solubilized species e.g., ions
  • second draw product stream 224 can have a solubilized ion concentration of 10 wt % and third concentrated aqueous stream 238 can have a solubilized ion concentration of 20 wt %, which is 2 times greater than the weight percentage of solubilized ions in the second draw product stream.
  • the third draw inlet stream (e.g., stream 234 in FIG. 2B ) can have an osmotic pressure that is at least about 1.01 times, at least about 1.1 times, at least about 1.5 times, at least about 2 times, at least about 5 times, at least about 10 times, or at least about 50 times (and/or, in some embodiments, up to about 100 times, up to about 500 times, up to about 1000 times, up to about 5000 times, or more) the osmotic pressure of the third draw product stream (e.g., stream 236 in FIG. 2B ).
  • the third draw inlet stream (e.g., stream 234 in FIG. 2B ) can have a weight percentage of solubilized species (e.g., ions) that is at least about 1.01 times, at least about 1.1 times, at least about 1.5 times, at least about 2 times, at least about 5 times, at least about 10 times, or at least about 50 times (and/or, in some embodiments, up to about 100 times, up to about 500 times, up to about 1000 times, up to about 5000 times, or more) the weight percentage of solubilized species (e.g., ions) in the third draw product stream (e.g., stream 236 in FIG. 2B ).
  • solubilized species e.g., ions
  • third draw product stream 236 can have a solubilized ion concentration of 8 wt % and third draw inlet stream 234 can have a solubilized ion concentration of 18 wt %, which is 2.25 times greater than the weight percentage of solubilized ions in the third draw product stream.
  • the third osmotic membrane separator can be operated as a reverse osmosis membrane separator, according to certain embodiments. That is to say, in some embodiments, water can be transported from the first side of the third osmotic membrane to the second side of the third osmotic membrane by applying a hydraulic pressure to the first side of the third osmotic membrane as a driving force, such that local osmotic pressure gradients through the thickness of the membrane that would otherwise favor the transport of water from the second side of the membrane to the first side of the membrane are overcome by the applied hydraulic pressure.
  • the osmotic pressure of the stream on the first side of the third osmotic membrane can be higher than the osmotic pressure of the stream on the second side of the third osmotic membrane, such that water is transported through the third osmotic membrane due to a hydraulic pressure applied to the first side of the third osmotic membrane.
  • System 260 in FIG. 2B comprises optional fourth osmotic membrane 240 , which comprises first side 242 and second side 244 .
  • Some embodiments comprise transporting at least a portion of the third draw product stream from the second side of the third osmotic membrane across a first side of a fourth osmotic membrane.
  • at least a portion of third draw product stream 236 is transported from second side 232 of third osmotic membrane 228 across first side 242 of fourth osmotic membrane 240 .
  • Certain embodiments comprise transporting a fourth draw inlet stream across a second side of the fourth osmotic membrane.
  • fourth draw inlet stream 246 is transported across second side 244 of fourth osmotic membrane 240 .
  • Some embodiments comprise applying a hydraulic pressure to the third draw product stream on the first side of the fourth osmotic membrane such that water is transported from the third draw product stream through the fourth osmotic membrane to the fourth draw inlet stream to produce a fourth draw product stream having a lower osmotic pressure (e.g., due to a lower molar concentration of solubilized species (e.g., ions)) than the fourth draw inlet stream and a fourth concentrated aqueous stream having a higher osmotic pressure (e.g., due to a higher molar concentration of solubilized species (e.g., ions)) than the third draw product stream.
  • a hydraulic pressure to the third draw product stream on the first side of the fourth osmotic membrane such that water is transported from the third draw product stream through the fourth osmotic membrane to the fourth draw inlet stream to produce a fourth draw product stream having a lower osmotic pressure (e.g., due to a lower molar concentration
  • a hydraulic pressure is applied to third draw product stream 236 on first side 242 of fourth osmotic membrane 240 such that water is transported from third draw product stream 236 through fourth osmotic membrane 240 to fourth draw inlet stream 246 to produce fourth draw product stream 248 having a lower osmotic pressure (e.g., due to a lower molar concentration of solubilized species (e.g., ions)) than fourth draw inlet stream 246 and fourth concentrated aqueous stream 250 having a higher osmotic pressure (e.g., due to a higher molar concentration of solubilized species (e.g., ions) than third draw product stream 236 .
  • the fourth concentrated aqueous stream (e.g., 250 in FIG. 2B ) can have an osmotic pressure that is at least about 1.01 times, at least about 1.1 times, at least about 1.5 times, at least about 2 times, at least about 5 times, at least about 10 times, or at least about 50 times (and/or, in some embodiments, up to about 100 times, up to about 500 times, up to about 1000 times, up to about 5000 times, or more) the osmotic pressure of the third draw product stream (e.g., stream 236 in FIG. 2B ).
  • the fourth concentrated aqueous stream (e.g., 250 in FIG. 2B ) can have a weight percentage of solubilized ions that is at least about 1.01 times, at least about 1.1 times, at least about 1.5 times, at least about 2 times, at least about 5 times, at least about 10 times, or at least about 50 times (and/or, in some embodiments, up to about 100 times, up to about 500 times, up to about 1000 times, up to about 5000 times, or more) the weight percentage of solubilized ions in the third draw product stream (e.g., stream 236 in FIG. 2B ).
  • the fourth draw inlet stream (e.g., stream 246 in FIG. 2B ) can have an osmotic pressure that is at least about 1.01 times, at least about 1.1 times, at least about 1.5 times, at least about 2 times, at least about 5 times, at least about 10 times, or at least about 50 times (and/or, in some embodiments, up to about 100 times, up to about 500 times, up to about 1000 times, up to about 5000 times, or more) the osmotic pressure of the fourth draw product stream (e.g., stream 248 in FIG. 2B ).
  • the fourth draw inlet stream (e.g., stream 246 in FIG. 2B ) can have a weight percentage of solubilized ions that is at least about 1.01 times, at least about 1.1 times, at least about 1.5 times, at least about 2 times, at least about 5 times, at least about 10 times, or at least about 50 times (and/or, in some embodiments, up to about 100 times, up to about 500 times, up to about 1000 times, up to about 5000 times, or more) the weight percentage of solubilized ions in the fourth draw product stream (e.g., stream 248 in FIG. 2B ).
  • the fourth osmotic membrane separator can be operated as a reverse osmosis membrane, according to certain embodiments. That is to say, in some embodiments, water can be transported from the first side of the fourth osmotic membrane to the second side of the fourth osmotic membrane by applying a hydraulic pressure to the first side of the fourth osmotic membrane as a driving force, such that local osmotic pressure gradients through the thickness of the membrane that would otherwise favor the transport of water from the second side of the membrane to the first side of the membrane are overcome by the applied hydraulic pressure.
  • the osmotic pressure of the stream on the first side of the fourth osmotic membrane can be higher than the osmotic pressure of the stream on the second side of the fourth osmotic membrane, such that water is transported through the fourth osmotic membrane due to a hydraulic pressure applied to the first side of the fourth osmotic membrane.
  • the transmembrane net driving force i.e., the net driving force through the thickness of the osmotic membrane
  • the transmembrane net driving force is defined as the difference between the transmembrane hydraulic pressure gradient and the transmembrane osmotic pressure gradient, as shown in Equation 1.
  • the transmembrane net driving force is uniform to within about 10%, within about 5%, within about 3%, within about 2%, or within about 1%.
  • the transmembrane net driving force at any given location across the facial area of the osmotic membrane is determined by measuring the properties of the streams on opposite sides of the osmotic membrane at that location. Specifically, one would measure the hydraulic pressure on opposite sides of the osmotic membrane at that location and the osmotic pressure on opposite sides of the osmotic membrane at that location.
  • the transmembrane net driving force could then be calculated using Equation 1 above. As a specific example, referring to FIG.
  • the transmembrane net driving force at point 150 of osmotic membrane 102 can be determined by measuring the hydraulic pressure of the stream on side 104 at point 150 (P 150 ); the osmotic pressure of the stream on side 104 at point 150 ( ⁇ 150 ); the hydraulic pressure of the stream on side 106 at point 152 (P 152 ), which is opposite point 150 ; and the osmotic pressure of the stream on side 106 at point 152 ( ⁇ 152 ).
  • the transmembrane net driving force at a particular location would be said to be uniform to within X % if the transmembrane net driving force at that location is within X % of the transmembrane net driving force spatially averaged over the facial area of the osmotic membrane (also referred to herein as the spatially-averaged transmembrane net driving force).
  • FIGS. 1C -ID To determine the spatially-averaged transmembrane net driving force across the facial area of an osmotic membrane, one would calculate the transmembrane net driving force (using Equation 1) at each point across the facial area of the osmotic membrane (to produce a two-dimensional distribution of transmembrane net driving forces) and spatially average the distribution of the transmembrane net driving force.
  • Equation 1 To illustrate an exemplary calculation, reference is made to FIGS. 1C -ID.
  • FIG. 1C is a front, top, right side perspective view of an osmotic membrane 102
  • FIG. 1D is a front, bottom, right side perspective view of the osmotic membrane 102 of FIG. 1C .
  • FIGS. 1C is a front, top, right side perspective view of an osmotic membrane 102
  • FIG. 1D is a front, bottom, right side perspective view of the osmotic membrane 102 of FIG. 1C .
  • osmotic membrane 102 includes first side 104 and second side 106 .
  • Osmotic membrane 102 also comprises a facial area 163 defined by dimensions 160 and 161 .
  • To determine the spatially-averaged transmembrane net driving force across facial area 163 of osmotic membrane 102 in FIGS. 1C-1D one would calculate the two-dimensional distribution of the transmembrane net driving force (using Equation 1) at each point across facial area 163 of osmotic membrane 102 . For example, in FIGS.
  • Equation 1 would be used to determine the transmembrane net driving force between points 150 A and 152 A, between points 150 B and 152 B, between points 150 C and 152 C, between points 150 D and 152 D, between points 150 E and 152 E, and at a statistically representative number of point pairs across facial area 163 until a 2-dimensional profile of the transmembrane net driving force is produced.
  • the spatially averaged transmembrane net driving force through membrane 102 would then be calculated by number averaging the transmembrane net driving forces at each point within the 2-dimensional profile.
  • the transmembrane net driving force can be made uniform, at least in part, by initiating (and/or selecting) appropriate operating conditions (e.g., mass flow rates, osmotic pressures, and/or hydraulic pressures) at the feed inlet and the draw inlet to the osmotic separators, as described in more detail below.
  • appropriate operating conditions e.g., mass flow rates, osmotic pressures, and/or hydraulic pressures
  • m D , i m F , i C ⁇ ⁇ F , i - ( P F - P D ) ⁇ D , i + ( P F - P D ) [ 4 ]
  • P F is the hydraulic pressure at the inlet of the feed stream (i.e., the stream entering the osmotic separator and from which water is removed during the osmosis process)
  • m F,i is the mass flow rate of the feed stream at the inlet of the feed stream to the osmotic membrane
  • ⁇ F,i is the osmotic pressure of the feed stream at the inlet of the feed stream to the osmotic membrane
  • P D is the hydraulic pressure at the inlet of the draw stream to the osmotic membrane (i.e., the stream entering the osmotic separator and into which water is added during the osmosis process)
  • m D,i is the mass flow rate of the draw stream at the inlet of the draw stream
  • C can be from about 0.9 to about 1.1, from about 0.95 to about 1.05, from about 0.98 to about 1.02, or from about 0.99 to about 1.01.
  • Equation 4 it is believed that operating osmotic membranes such that they satisfy Equation 4 above can reduce (e.g., minimize) entropy generation and establish substantially uniform local fluxes of water through the osmotic membrane, which can reduce the amount of energy wasted during the osmosis process.
  • the mass flow rates, hydraulic pressures, and osmotic pressures of incoming streams should be measured as bulk mass flow rates, bulk hydraulic pressures, and bulk osmotic pressures of the incoming liquids at their point of entry to the osmotic separator.
  • Bulk hydraulic pressure (which is generally measured as a gauge pressure) can be measured, for example, using a pressure transducer, a Bourdon tube, a diaphragm pressure gauge, or any other suitable pressure gauge.
  • Mass flow rates may be determined using any of a number of suitable flow meters known to those of ordinary skill in the art.
  • the bulk osmotic pressure of a stream may be determined, for example, by measuring the osmotic pressure (e.g., using any of the methods described elsewhere herein) of a sample of the stream.
  • the osmotic separator comprising osmotic membrane 102 can be operated such that:
  • the first osmotic separator (comprising the first osmotic membrane) can be operated such that it satisfies Equation 4 above.
  • the first osmotic separator comprising first osmotic membrane 202 can be operated such that:
  • m 210 m 208 C ⁇ ⁇ 208 - ( P 208 - P 210 ) ⁇ 210 + ( P 208 - P 210 ) [ 4 ⁇ B ]
  • P 208 is the bulk hydraulic pressure of stream 208 as it enters the first osmotic separator
  • m 208 is the bulk mass flow rate of stream 208 as it enters the first osmotic separator
  • ⁇ 208 is the bulk osmotic pressure of stream 208 as it enters the first osmotic separator
  • P 210 is the bulk hydraulic pressure of stream 210 as it enters the first osmotic separator
  • m 210 is the bulk mass flow rate of stream 210 as it enters the first osmotic separator
  • ⁇ 210 is the bulk osmotic pressure of stream 210 as it enters the first osmotic separator
  • C is from about 0.8 to about 1.2.
  • C can be from about 0.9 to about 1.1,
  • the second osmotic separator (comprising the second osmotic membrane) can be operated such that it satisfies Equation 4 above.
  • the second osmotic separator comprising second osmotic membrane 216 can be operated such that:
  • m 222 m 212 C ⁇ ⁇ 212 - ( P 212 - P 222 ) ⁇ 222 + ( P 212 - P 222 ) [ 4 ⁇ C ]
  • P 212 is the bulk hydraulic pressure of stream 212 as it enters the second osmotic separator
  • m 212 is the bulk mass flow rate of stream 212 as it enters the second osmotic separator
  • ⁇ 212 is the bulk osmotic pressure of stream 212 as it enters the second osmotic separator
  • P 222 is the bulk hydraulic pressure of stream 222 as it enters the second osmotic separator
  • m 222 is the bulk mass flow rate of stream 222 as it enters the second osmotic separator
  • ⁇ 222 is the bulk osmotic pressure of stream 222 as it enters the second osmotic separator
  • C is from about 0.8 to about 1.2.
  • C can be from about 0.9 to about 1.1,
  • the third osmotic separator (comprising the third osmotic membrane) can be operated such that it satisfies Equation 4 above.
  • the third osmotic separator comprising third osmotic membrane 228 can be operated such that:
  • m 234 m 224 C ⁇ ⁇ 224 - ( P 224 - P 234 ) ⁇ 234 + ( P 224 - P 234 ) [ 4 ⁇ D ]
  • P 224 is the bulk hydraulic pressure of stream 224 as it enters the third osmotic separator
  • m 224 is the bulk mass flow rate of stream 224 as it enters the third osmotic separator
  • ⁇ 224 is the bulk osmotic pressure of stream 224 as it enters the third osmotic separator
  • P 234 is the bulk hydraulic pressure of stream 234 as it enters the third osmotic separator
  • m 234 is the bulk mass flow rate of stream 234 as it enters the third osmotic separator
  • ⁇ 234 is the bulk osmotic pressure of stream 234 as it enters the third osmotic separator
  • C is from about 0.8 to about 1.2. In certain embodiments, C can be from about 0.9 to about
  • the fourth osmotic separator (comprising the fourth osmotic membrane) can be operated such that it satisfies Equation 4 above.
  • the fourth osmotic separator comprising fourth osmotic membrane 240 can be operated such that:
  • m 246 m 236 C ⁇ ⁇ 236 - ( P 236 - P 246 ) ⁇ 246 + ( P 236 - P 246 ) [ 4 ⁇ E ]
  • P 236 is the bulk hydraulic pressure of stream 236 as it enters the fourth osmotic separator
  • m 236 is the bulk mass flow rate of stream 236 as it enters the fourth osmotic separator
  • ⁇ 236 is the bulk osmotic pressure of stream 236 as it enters the fourth osmotic separator
  • P 246 is the bulk hydraulic pressure of stream 246 as it enters the fourth osmotic separator
  • m 246 is the bulk mass flow rate of stream 246 as it enters the fourth osmotic separator
  • ⁇ 246 is the bulk osmotic pressure of stream 246 as it enters the fourth osmotic separator
  • C is from about 0.8 to about 1.2. In certain embodiments, C can be from about 0.9 to about
  • Certain embodiments comprise directing the transport of an aqueous feed stream across an osmotic membrane and/or a draw inlet stream across an osmotic membrane such that the following two ratios are within about 20% of each other (and/or, in some embodiments, within about 10% of each other, within about 5% of each other, within about 3% of each other, within about 2% of each other, or within about 1% of each other): a ratio of a mass flow rate of the draw inlet stream entering the osmotic membrane to a mass flow rate of the aqueous feed stream entering the osmotic membrane; and a ratio of the difference between the osmotic pressure of the aqueous feed stream entering the osmotic membrane and the inlet pressure difference across the osmotic membrane to the sum of the osmotic pressure of the draw inlet stream entering the osmotic membrane and the inlet pressure difference across the osmotic membrane.
  • the inlet pressure difference across an osmotic membrane corresponds to the difference between the hydraulic pressure at the inlet of the feed stream (also referred to herein as P F ) and the hydraulic pressure at the inlet of the draw stream to the osmotic membrane (also referred to herein as P D ).
  • P F hydraulic pressure at the inlet of the feed stream
  • P D hydraulic pressure at the inlet of the draw stream to the osmotic membrane
  • the ratio of a mass flow rate of the draw inlet stream entering the osmotic membrane (also referred to herein as m D,i ) to a mass flow rate of the aqueous feed stream entering the osmotic membrane (also referred to herein as m F,i ) can be calculated by dividing the mass flow rate of the draw inlet stream entering the osmotic membrane by the mass flow rate of the aqueous feed stream entering the osmotic membrane (and, thus, may be expressed as m D,i /m F,i ).
  • ratio of the difference between the osmotic pressure of the aqueous feed stream entering the osmotic membrane and the inlet pressure difference across the osmotic membrane (also referred to herein as ⁇ F,i ⁇ (P F ⁇ P D )) to the sum of the osmotic pressure of the draw inlet stream entering the osmotic membrane and the inlet pressure difference across the osmotic membrane (also referred to herein as ⁇ D,i +(P F ⁇ P D ))
  • ⁇ D,i +(P F ⁇ P D ) can be calculated by dividing the difference between the osmotic pressure of the aqueous feed stream entering the osmotic membrane and the inlet pressure difference across the osmotic membrane by the sum of the osmotic pressure of the draw inlet stream entering the osmotic membrane and the inlet pressure difference across the osmotic membrane (and, thus, may be expressed as [( ⁇ F,I ⁇ (P F ⁇
  • the mass flow rates, hydraulic pressures, and osmotic pressures of incoming streams should be measured as bulk mass flow rates, bulk hydraulic pressures, and bulk osmotic pressures of the incoming liquids at their place of entry to the osmotic separator.
  • certain embodiments comprise directing the transport of aqueous feed stream 108 across osmotic membrane 102 and/or draw inlet stream 110 across osmotic membrane 102 such that the following two ratios are within 20% of each other (and/or, in some embodiments, within about 10% of each other, within about 5% of each other, within about 3% of each other, within about 2% of each other, or within about 1% of each other): the ratio of the mass flow rate of draw inlet stream 110 entering osmotic membrane 102 to the mass flow rate of aqueous feed stream 108 entering osmotic membrane 102 ; and the ratio of the difference between the osmotic pressure of aqueous feed stream 108 entering osmotic membrane 102 and the inlet pressure difference across osmotic membrane 102 to the sum of the osmotic pressure of draw inlet stream 110 entering osmotic membrane 102 and the inlet pressure difference across osmotic membrane 102 .
  • the inlet pressure difference across osmotic membrane 102 can be determined by subtracting the hydraulic pressure of draw inlet stream 110 at the inlet of draw inlet stream 110 to osmotic membrane 102 from the hydraulic pressure of aqueous feed stream 108 at the inlet of aqueous feed stream 108 to osmotic membrane 102 .
  • the first osmotic separator (comprising the first osmotic membrane) can be operated such that the ratios described above are relatively close to each other.
  • certain embodiments comprise directing the transport of aqueous feed stream 208 across first osmotic membrane 202 and/or first draw inlet stream 210 across first osmotic membrane 202 such that the following two ratios are within 20% of each other (and/or, in some embodiments, within about 10% of each other, within about 5% of each other, within about 3% of each other, within about 2% of each other, or within about 1% of each other): the ratio of the mass flow rate of first draw inlet stream 210 entering first osmotic membrane 202 to the mass flow rate of aqueous feed stream 208 entering first osmotic membrane 202 ; and the ratio of the difference between the osmotic pressure of aqueous feed stream 208 entering first osmotic membrane 202
  • the inlet pressure difference across first osmotic membrane 202 can be determined by subtracting the hydraulic pressure of first draw inlet stream 210 at the inlet of first draw inlet stream 210 to first osmotic membrane 202 from the hydraulic pressure of aqueous feed stream 208 at the inlet of aqueous feed stream 208 to first osmotic membrane 202 .
  • the second osmotic separator (comprising the second osmotic membrane) can be operated such that the ratios described above are relatively close to each other.
  • certain embodiments comprise directing the transport of first draw product stream 212 across second osmotic membrane 216 and/or second draw inlet stream 222 across second osmotic membrane 216 such that the following two ratios are within 20% of each other (and/or, in some embodiments, within about 10% of each other, within about 5% of each other, within about 3% of each other, within about 2% of each other, or within about 1% of each other): the ratio of the mass flow rate of second draw inlet stream 222 entering second osmotic membrane 216 to the mass flow rate of first draw product stream 212 entering second osmotic membrane 216 ; and the ratio of the difference between the osmotic pressure of first draw product stream 212 entering second osmotic membrane 216 and the inlet pressure difference
  • the inlet pressure difference across second osmotic membrane 216 can be determined by subtracting the hydraulic pressure of second draw inlet stream 222 at the inlet of second draw inlet stream 222 to second osmotic membrane 216 from the hydraulic pressure of first draw product stream 212 at the inlet of first draw product stream 212 to second osmotic membrane 216 .
  • the third osmotic separator (comprising the third osmotic membrane) can be operated such that the ratios described above are relatively close to each other.
  • certain embodiments comprise directing the transport of second draw product stream 224 across third osmotic membrane 228 and/or third draw inlet stream 234 across third osmotic membrane 228 such that the following two ratios are within 20% of each other (and/or, in some embodiments, within about 10% of each other, within about 5% of each other, within about 3% of each other, within about 2% of each other, or within about 1% of each other): the ratio of the mass flow rate of third draw inlet stream 234 entering third osmotic membrane 228 to the mass flow rate of second draw product stream 224 entering third osmotic membrane 228 ; and the ratio of the difference between the osmotic pressure of second draw product stream 224 entering third osmotic membrane 228 and the inlet pressure difference across third
  • the inlet pressure difference across third osmotic membrane 228 can be determined by subtracting the hydraulic pressure of third draw inlet stream 234 at the inlet of third draw inlet stream 234 to third osmotic membrane 228 from the hydraulic pressure of second draw product stream 224 at the inlet of second draw product stream 224 to third osmotic membrane 228 .
  • the fourth osmotic separator (comprising the fourth osmotic membrane) can be operated such that the ratios described above are relatively close to each other.
  • certain embodiments comprise directing the transport of third draw product stream 236 across third osmotic membrane 240 and/or fourth draw inlet stream 246 across fourth osmotic membrane 240 such that the following two ratios are within 20% of each other (and/or, in some embodiments, within about 10% of each other, within about 5% of each other, within about 3% of each other, within about 2% of each other, or within about 1% of each other): the ratio of the mass flow rate of fourth draw inlet stream 246 entering fourth osmotic membrane 240 to the mass flow rate of third draw product stream 236 entering fourth osmotic membrane 240 ; and the ratio of the difference between the osmotic pressure of third draw product stream 236 entering fourth osmotic membrane 240 and the inlet pressure difference across fourth
  • the inlet pressure difference across fourth osmotic membrane 240 can be determined by subtracting the hydraulic pressure of fourth draw inlet stream 246 at the inlet of fourth draw inlet stream 246 to fourth osmotic membrane 240 from the hydraulic pressure of third draw product stream 236 at the inlet of third draw product stream 236 to fourth osmotic membrane 240 .
  • Certain embodiments comprise directing the transport of an aqueous feed stream across an osmotic membrane and/or a draw inlet stream across the osmotic membrane such that the transmembrane net driving force at the entrance of the aqueous feed stream to the osmotic membrane and the transmembrane net driving force at the entrance of the draw inlet stream to the osmotic membrane are within about 10% of each other (and/or, in some embodiments, within about 5% of each other, within about 3% of each other, within about 2% of each other, or within about 1% of each other).
  • the transmembrane net driving force at a particular location along an osmotic membrane can be calculated using Equation 1, as described above.
  • certain embodiments comprise directing the transport of aqueous feed stream 108 across osmotic membrane 102 and/or draw inlet stream 110 across osmotic membrane 102 such that the transmembrane net driving force at the entrance of aqueous feed stream 108 to osmotic membrane 102 and the transmembrane net driving force at the entrance of draw inlet stream 110 to osmotic membrane 102 are within about 10% of each other (and/or, in some embodiments, within about 5% of each other, within about 3% of each other, within about 2% of each other, or within about 1% of each other).
  • the first osmotic separator (comprising the first osmotic membrane) can be operated such that the transmembrane net driving forces at the inlets to the first osmotic membrane are relatively close to each other. For example, referring to FIGS.
  • certain embodiments comprise directing the transport of aqueous feed stream 208 across first osmotic membrane 202 and/or first draw inlet stream 210 across first osmotic membrane 202 such that the transmembrane net driving force at the entrance of aqueous feed stream 208 to first osmotic membrane 202 and the transmembrane net driving force at the entrance of first draw inlet stream 210 to first osmotic membrane 202 are within about 10% of each other (and/or, in some embodiments, within about 5% of each other, within about 3% of each other, within about 2% of each other, or within about 1% of each other).
  • the second osmotic separator (comprising the second osmotic membrane) can be operated such that the transmembrane net driving forces at the inlets to the second osmotic membrane are relatively close to each other. For example, referring to FIGS.
  • certain embodiments comprise directing the transport of first draw product stream 212 across second osmotic membrane 216 and/or second draw inlet stream 222 across second osmotic membrane 216 such that the transmembrane net driving force at the entrance of first draw product stream 212 to second osmotic membrane 216 and the transmembrane net driving force at the entrance of second draw inlet stream 222 to second osmotic membrane 216 are within about 10% of each other (and/or, in some embodiments, within about 5% of each other, within about 3% of each other, within about 2% of each other, or within about 1% of each other).
  • the third osmotic separator (comprising the third osmotic membrane) can be operated such that the transmembrane net driving forces at the inlets to the third osmotic membrane are relatively close to each other. For example, referring to FIG.
  • certain embodiments comprise directing the transport of second draw product stream 224 across third osmotic membrane 228 and/or third draw inlet stream 234 across third osmotic membrane 228 such that the transmembrane net driving force at the entrance of second draw product stream 224 to third osmotic membrane 228 and the transmembrane net driving force at the entrance of third draw inlet stream 234 to third osmotic membrane 228 are within about 10% of each other (and/or, in some embodiments, within about 5% of each other, within about 3% of each other, within about 2% of each other, or within about 1% of each other).
  • the fourth osmotic separator (comprising the fourth osmotic membrane) can be operated such that the transmembrane net driving forces at the inlets to the fourth osmotic membrane are relatively close to each other. For example, referring to FIG.
  • certain embodiments comprise directing the transport of third draw product stream 236 across fourth osmotic membrane 240 and/or fourth draw inlet stream 246 across fourth osmotic membrane 240 such that the transmembrane net driving force at the entrance of third draw product stream 236 to fourth osmotic membrane 240 and the transmembrane net driving force at the entrance of fourth draw inlet stream 246 to fourth osmotic membrane 240 are within about 10% of each other (and/or, in some embodiments, within about 5% of each other, within about 3% of each other, within about 2% of each other, or within about 1% of each other).
  • the transmembrane net driving force at the inlet(s) to an osmotic membrane can be controlled, initiated, and/or selected, for example, by selecting appropriate operating conditions (e.g., mass flow rates, osmotic pressures (e.g., via solubilized species selection and/or concentration), and/or hydraulic pressures) of the flow streams.
  • appropriate operating conditions e.g., mass flow rates, osmotic pressures (e.g., via solubilized species selection and/or concentration), and/or hydraulic pressures) of the flow streams.
  • one or more osmotic membranes can be operated such that the transmembrane net driving forces at the inlets to the osmotic membrane are initially relatively unbalanced, after which, operation of the system may be adjusted such that the transmembrane net driving forces at the inlets to the osmotic membrane are relatively balanced.
  • some embodiments comprise directing the transport of the aqueous feed stream across the osmotic membrane and/or the draw inlet stream across the osmotic membrane such that the transmembrane net driving force at the entrance of the aqueous feed stream to the osmotic membrane and the transmembrane net driving force at the entrance of the draw inlet stream to the osmotic membrane are at least about 10% different from each other (and/or, in some embodiments, at least about 11%, at least about 12%, at least about 15%, at least about 20%, at least about 50%, or at least about 100% different from each other).
  • Some such embodiments comprise measuring at least one of a temperature, a pressure, a solubilized species concentration, and a flow rate of the aqueous feed stream and/or the draw inlet stream. Some such embodiments comprise changing at least one of the flow rate of the aqueous feed stream and the flow rate of the draw inlet stream such that the transmembrane driving force at the entrance of the aqueous feed stream to the osmotic membrane and the transmembrane driving force at the entrance of the draw inlet stream to the osmotic membrane are within about 10% of each other (and/or, in some embodiments, within about 5%, within about 3%, within about 2%, or within about 1% of each other).
  • certain embodiments comprise directing the transport of aqueous feed stream 108 across osmotic membrane 102 and/or draw inlet stream 110 across osmotic membrane 102 such that the transmembrane net driving force at the entrance of aqueous feed stream 108 to osmotic membrane 102 and the transmembrane driving force at the entrance of draw inlet stream 110 to osmotic membrane 102 are at least about 10% different from each other (and/or, in some embodiments, at least about 11%, at least about 12%, at least about 15%, at least about 20%, at least about 50%, or at least about 100% different from each other).
  • Some such embodiments comprise measuring at least one of a temperature, a pressure, a solubilized species concentration, and a flow rate of aqueous feed stream 108 and/or draw inlet stream 110 . Some such embodiments comprise changing at least one of the flow rate of aqueous feed stream 108 and the flow rate of draw inlet stream 110 such that the transmembrane driving force at the entrance of aqueous feed stream 108 to osmotic membrane 102 and the transmembrane driving force at the entrance of draw inlet stream 110 to osmotic membrane 102 are within about 10% of each other (and/or, in some embodiments, within about 5%, within about 3%, within about 2%, or within about 1% of each other).
  • the first osmotic separator (comprising the first osmotic membrane) can be operated such that the transmembrane net driving forces at the inlets to the first osmotic membrane are initially relatively unbalanced, after which, operation of the system may be adjusted such that the transmembrane net driving forces at the inlets to the first osmotic membrane are relatively balanced.
  • operation of the system may be adjusted such that the transmembrane net driving forces at the inlets to the first osmotic membrane are relatively balanced.
  • certain embodiments comprise directing the transport of aqueous feed stream 208 across first osmotic membrane 202 and/or first draw inlet stream 210 across first osmotic membrane 202 such that the transmembrane net driving force at the entrance of aqueous feed stream 208 to first osmotic membrane 202 and the transmembrane driving force at the entrance of first draw inlet stream 210 to first osmotic membrane 202 are at least about 10% different from each other (and/or, in some embodiments, at least about 11%, at least about 12%, at least about 15%, at least about 20%, at least about 50%, or at least about 100% different from each other).
  • Some such embodiments comprise measuring at least one of a temperature, a pressure, a solubilized species concentration, and a flow rate of aqueous feed stream 208 and/or first draw inlet stream 210 . Some such embodiments comprise changing at least one of the flow rate of aqueous feed stream 208 and the flow rate of first draw inlet stream 210 such that the transmembrane driving force at the entrance of aqueous feed stream 208 to first osmotic membrane 202 and the transmembrane driving force at the entrance of first draw inlet stream 210 to first osmotic membrane 202 are within about 10% of each other (and/or, in some embodiments, within about 5%, within about 3%, within about 2%, or within about 1% of each other).
  • the second osmotic separator (comprising the second osmotic membrane) can be operated such that the transmembrane net driving forces at the inlets to the second osmotic membrane are initially relatively unbalanced, after which, operation of the system may be adjusted such that the transmembrane net driving forces at the inlets to the second osmotic membrane are relatively balanced.
  • operation of the system may be adjusted such that the transmembrane net driving forces at the inlets to the second osmotic membrane are relatively balanced.
  • certain embodiments comprise directing the transport of first draw product stream 212 across second osmotic membrane 216 and/or second draw inlet stream 222 across second osmotic membrane 216 such that the transmembrane net driving force at the entrance of first draw product stream 212 to second osmotic membrane 216 and the transmembrane driving force at the entrance of second draw inlet stream 222 to second osmotic membrane 216 are at least about 10% different from each other (and/or, in some embodiments, at least about 11%, at least about 12%, at least about 15%, at least about 20%, at least about 50%, or at least about 100% different from each other).
  • Some such embodiments comprise measuring at least one of a temperature, a pressure, a solubilized species concentration, and a flow rate of first draw product stream 212 and/or second draw inlet stream 222 . Some such embodiments comprise changing at least one of the flow rate of first draw product stream 212 and the flow rate of second draw inlet stream 222 such that the transmembrane driving force at the entrance of first draw product stream 212 to second osmotic membrane 216 and the transmembrane driving force at the entrance of second draw inlet stream 222 to second osmotic membrane 216 are within about 10% of each other (and/or, in some embodiments, within about 5%, within about 3%, within about 2%, or within about 1% of each other).
  • the third osmotic separator (comprising the third osmotic membrane) can be operated such that the transmembrane net driving forces at the inlets to the third osmotic membrane are initially relatively unbalanced, after which, operation of the system may be adjusted such that the transmembrane net driving forces at the inlets to the third osmotic membrane are relatively balanced.
  • operation of the system may be adjusted such that the transmembrane net driving forces at the inlets to the third osmotic membrane are relatively balanced.
  • certain embodiments comprise directing the transport of second draw product stream 224 across third osmotic membrane 228 and/or third draw inlet stream 234 across third osmotic membrane 228 such that the transmembrane net driving force at the entrance of second draw product stream 224 to third osmotic membrane 228 and the transmembrane driving force at the entrance of third draw inlet stream 234 to third osmotic membrane 228 are at least about 10% different from each other (and/or, in some embodiments, at least about 11%, at least about 12%, at least about 15%, at least about 20%, at least about 50%, or at least about 100% different from each other).
  • Some such embodiments comprise measuring at least one of a temperature, a pressure, a solubilized species concentration, and a flow rate of second draw product stream 224 and/or third draw inlet stream 234 . Some such embodiments comprise changing at least one of the flow rate of second draw product stream 224 and the flow rate of third draw inlet stream 234 such that the transmembrane driving force at the entrance of second draw product stream 224 to third osmotic membrane 228 and the transmembrane driving force at the entrance of third draw inlet stream 234 to third osmotic membrane 228 are within about 10% of each other (and/or, in some embodiments, within about 5%, within about 3%, within about 2%, or within about 1% of each other).
  • the fourth osmotic separator (comprising the fourth osmotic membrane) can be operated such that the transmembrane net driving forces at the inlets to the fourth osmotic membrane are initially relatively unbalanced, after which, operation of the system may be adjusted such that the transmembrane net driving forces at the inlets to the fourth osmotic membrane are relatively balanced.
  • operation of the system may be adjusted such that the transmembrane net driving forces at the inlets to the fourth osmotic membrane are relatively balanced.
  • certain embodiments comprise directing the transport of third draw product stream 236 across fourth osmotic membrane 240 and/or fourth draw inlet stream 246 across fourth osmotic membrane 240 such that the transmembrane net driving force at the entrance of third draw product stream 236 to fourth osmotic membrane 240 and the transmembrane driving force at the entrance of fourth draw inlet stream 246 to fourth osmotic membrane 240 are at least about 10% different from each other (and/or, in some embodiments, at least about 11%, at least about 12%, at least about 15%, at least about 20%, at least about 50%, or at least about 100% different from each other).
  • Some such embodiments comprise measuring at least one of a temperature, a pressure, a solubilized species concentration, and a flow rate of third draw product stream 236 and/or fourth draw inlet stream 246 . Some such embodiments comprise changing at least one of the flow rate of third draw product stream 236 and the flow rate of fourth draw inlet stream 246 such that the transmembrane driving force at the entrance of third draw product stream 236 to fourth osmotic membrane 240 and the transmembrane driving force at the entrance of fourth draw inlet stream 246 to fourth osmotic membrane 240 are within about 10% of each other (and/or, in some embodiments, within about 5%, within about 3%, within about 2%, or within about 1% of each other).
  • the linear flow rate of water through the thickness of the osmotic membrane i.e., the transmembrane linear flow rate of water
  • the linear flow rate of water through the thickness of the osmotic membrane is spatially uniform across the facial area of the osmotic membrane.
  • One of ordinary skill in the art would be capable of determining the transmembrane linear flow rate of water at various points across the facial area of the osmotic membrane during operation, for example, by measuring concentrations of streams on each side of the osmotic membrane at various locations and performing a mass balance on the osmotic membrane.
  • the transmembrane linear flow rate of water is uniform to within about 20%, within about 10%, within about 5%, within about 3%, within about 2%, or within about 1%.
  • the percentage of facial area over which the transmembrane linear flow rate of water is spatially uniform one would use a similar procedure as described above with respect to the uniformity of the transmembrane net driving force.
  • transmembrane linear flow rates of water at points across the two-dimensional facial area of the osmotic membrane e.g., at points across facial area 163 shown in FIG. 1C , defined by dimensions 160 and 161 ).
  • the transmembrane linear flow rate of water at a particular location on the osmotic membrane would be said to be uniform to within X % if the transmembrane linear flow rate of water at that location is within X % of the spatially-averaged transmembrane linear flow rate of water.
  • transmembrane linear flow rate of water To determine the spatially-averaged transmembrane linear flow rate of water, one would determine the transmembrane linear flow rate of water at each point across the facial area of the osmotic membrane (to produce a two-dimensional distribution) and spatially average the distribution of the transmembrane linear flow rates of water. Without wishing to be bound by any particular theory, it is believed that operation of one or more osmotic membranes such that the linear flow rate of water is relatively spatially uniform across the membrane can produce relatively uniform water flux across the facial area of the membrane, which can lead to reductions in thermodynamic losses during operation of the membrane.
  • the streams on either side of an osmotic membrane can be operated in counter-current configuration. Operation of the desalination system in this manner can, according to certain but not necessarily all embodiments, allow one to more easily ensure that the transmembrane net driving force is spatially uniform across the facial area of the osmotic membrane.
  • An example of counter-current flow is illustrated in FIG. 1B , in which aqueous feed stream 108 is transported across first side 104 of osmotic membrane 102 in the direction of arrow 103 while draw inlet stream 110 is transported across second side 106 of osmotic membrane 102 in the direction of arrow 105 .
  • the primary flow directions of two streams that are in a counter-current flow configuration can form an angle of up to about 10° (or, in some cases, up to about 5°, up to about 2°, or up to about 10).
  • the aqueous feed stream and the first draw inlet stream are transported across the first osmotic membrane in a counter-current configuration.
  • the first draw product stream and the second draw inlet stream are transported across the second osmotic membrane in a counter-current configuration.
  • the second draw product stream and the third draw inlet stream are transported across the third osmotic membrane in a counter-current configuration. In some embodiments, the third draw product stream and the fourth draw inlet stream are transported across the fourth osmotic membrane in a counter-current configuration.
  • streams within the desalination system can be recycled.
  • at least a portion of the second concentrated aqueous stream is recycled to the second side of the first osmotic membrane.
  • the first draw inlet stream contains at least a portion of the second concentrated aqueous stream.
  • at least a portion of stream 226 can be recycled to second side 206 of osmotic membrane 202 , in some embodiments.
  • first draw inlet stream 210 can contain at least a portion of second concentrated aqueous stream 226 , as indicated by the dotted line connecting streams 226 and 210 .
  • the second draw inlet stream contains at least a portion of the third concentrated aqueous stream.
  • the second draw inlet stream contains at least a portion of the third concentrated aqueous stream.
  • at least a portion of stream 238 can be recycled to second side 220 of osmotic membrane 216 , in some embodiments.
  • second draw inlet stream 222 can contain at least a portion of third concentrated aqueous stream 238 , as indicated by the dotted line connecting streams 238 and 222 .
  • at least a portion of the fourth concentrated aqueous stream is recycled to the second side of the third osmotic membrane.
  • the third draw inlet stream contains at least a portion of the fourth concentrated aqueous stream.
  • at least a portion of stream 250 can be recycled to second side 232 of osmotic membrane 228 , in some embodiments.
  • third draw inlet stream 234 can contain at least a portion of fourth concentrated aqueous stream 250 , as indicated by the dotted line connecting streams 250 and 234 . Recycling of the streams in this manner can, according to certain although not necessarily all embodiments, simplify operation of the desalination system, reduce the volume of waste generated by the desalination system, and allow steady-state operation to be achieved more easily.
  • One advantage of certain, although not necessarily all, embodiments is that one or more of the osmotic-membrane-based desalination steps can be performed to achieve a desired degree of desalination while using relatively low transmembrane osmotic pressure gradients.
  • Such low transmembrane osmotic pressure gradients can be advantageous, for example, in certain cases in which reverse osmosis is used to perform desalination, as relatively low transmembrane osmotic pressure gradients can allow one to perform separations using relatively low applied hydraulic pressures, thus potentially reducing energy requirements and/or equipment costs compared to higher hydraulic pressure applications.
  • the difference between an osmotic pressure on a first side of the first osmotic membrane and an osmotic pressure on a second side of the first osmotic membrane is less than about 45 bar, less than about 40 bar, less than about 35 bar, less than about 30 bar, less than about 25 bar, less than about 20 bar, or less (and/or, in some embodiments, at least about 1 bar, at least about 2 bar, at least about 5 bar, at least about 10 bar, or more).
  • the difference between an osmotic pressure on first side 204 of first osmotic membrane 202 and an osmotic pressure on second side 206 of first osmotic membrane 202 is less than about 45 bar, less than about 40 bar, less than about 35 bar, less than about 30 bar, less than about 25 bar, less than about 20 bar, or less (and/or, in some embodiments, at least about 1 bar, at least about 2 bar, at least about 5 bar, at least about 10 bar, or more).
  • Relatively low transmembrane osmotic pressure gradients can also be present, in some embodiments, across the second, third, fourth, and/or additional osmotic membranes.
  • the difference between the osmotic pressure on a first side of the second osmotic membrane and an osmotic pressure on a second side of the second osmotic membrane is less than about 45 bar, less than about 40 bar, less than about 35 bar, less than about 30 bar, less than about 25 bar, less than about 20 bar, or less (and/or, in some embodiments, at least about 1 bar, at least about 2 bar, at least about 5 bar, at least about 10 bar, or more).
  • the difference between an osmotic pressure on first side 218 of second osmotic membrane 216 and an osmotic pressure on second side 220 of second osmotic membrane 216 is less than about 45 bar, less than about 40 bar, less than about 35 bar, less than about 30 bar, less than about 25 bar, less than about 20 bar, or less (and/or, in some embodiments, at least about 1 bar, at least about 2 bar, at least about 5 bar, at least about 10 bar, or more).
  • the difference between the osmotic pressure on a first side of the third osmotic membrane and an osmotic pressure on a second side of the third osmotic membrane is less than about 45 bar, less than about 40 bar, less than about 35 bar, less than about 30 bar, less than about 25 bar, less than about 20 bar, or less (and/or, in some embodiments, at least about 1 bar, at least about 2 bar, at least about 5 bar, at least about 10 bar, or more).
  • the difference between the osmotic pressure on a first side of the third osmotic membrane and an osmotic pressure on a second side of the third osmotic membrane is less than about 45 bar, less than about 40 bar, less than about 35 bar, less than about 30 bar, less than about 25 bar, less than about 20 bar, or less (and/or, in some embodiments, at least about 1 bar, at least about 2 bar, at least about 5 bar, at least about 10 bar, or more).
  • the difference between an osmotic pressure on first side 230 of third osmotic membrane 228 and an osmotic pressure on second side 232 of third osmotic membrane 228 is less than about 45 bar, less than about 40 bar, less than about 35 bar, less than about 30 bar, less than about 25 bar, less than about 20 bar, or less (and/or, in some embodiments, at least about 1 bar, at least about 2 bar, at least about 5 bar, at least about 10 bar, or more).
  • the difference between the osmotic pressure on a first side of the fourth osmotic membrane and an osmotic pressure on a second side of the fourth osmotic membrane is less than about 45 bar, less than about 40 bar, less than about 35 bar, less than about 30 bar, less than about 25 bar, less than about 20 bar, or less (and/or, in some embodiments, at least about 1 bar, at least about 2 bar, at least about 5 bar, at least about 10 bar, or more).
  • the difference between the osmotic pressure on a first side of the fourth osmotic membrane and an osmotic pressure on a second side of the fourth osmotic membrane is less than about 45 bar, less than about 40 bar, less than about 35 bar, less than about 30 bar, less than about 25 bar, less than about 20 bar, or less (and/or, in some embodiments, at least about 1 bar, at least about 2 bar, at least about 5 bar, at least about 10 bar, or more).
  • the difference between an osmotic pressure on first side 242 of fourth osmotic membrane 240 and an osmotic pressure on second side 244 of fourth osmotic membrane 240 is less than about 45 bar, less than about 40 bar, less than about 35 bar, less than about 30 bar, less than about 25 bar, less than about 20 bar, or less (and/or, in some embodiments, at least about 1 bar, at least about 2 bar, at least about 5 bar, at least about 10 bar, or more).
  • the transmembrane osmotic pressure gradient spatially-averaged across the facial area of one or more of the osmotic membranes e.g., the first osmotic membrane such as membrane 202 in FIGS. 2A-2B , the second osmotic membrane such as membrane 216 in FIGS. 2A-2B , the third osmotic membrane such as membrane 228 in FIG. 2B , and/or the fourth osmotic membrane such as membrane 240 in FIG. 2B
  • the first osmotic membrane such as membrane 202 in FIGS. 2A-2B
  • the second osmotic membrane such as membrane 216 in FIGS. 2A-2B
  • the third osmotic membrane such as membrane 228 in FIG. 2B
  • the fourth osmotic membrane such as membrane 240 in FIG. 2B
  • the spatially-averaged transmembrane osmotic pressure gradient across a facial area of a particular osmotic membrane can be calculated using a similar methodology as the calculation of the spatially-averaged transmembrane net driving force described above. For example, one can measure the osmotic pressure at all points along the facial area of the first side of the osmotic membrane, measure the osmotic pressure at all points along the facial area of the second side of the osmotic membrane, and calculate the two-dimensional distribution (across the facial area of the membrane) of the transmembrane osmotic pressure gradient (by subtracting, at each point across the facial area of the osmotic membrane, the osmotic pressure on the second side of the osmotic membrane from the osmotic pressure on the opposite point on the first side of the osmotic membrane).
  • FIGS. 1C-1D To illustrate an exemplary calculation of the spatially-averaged transmembrane osmotic pressure gradient, reference is made to FIGS. 1C-1D .
  • To determine the spatially-averaged transmembrane osmotic pressure gradient across facial area 163 of membrane 102 in FIGS. 1C-1D one would calculate the two-dimensional distribution of the transmembrane osmotic pressure gradient (i.e., ( ⁇ 1 ⁇ 2 )) at each point across facial area 163 of osmotic membrane 102 .
  • the osmotic pressures would be determined at a point on a first side of the osmotic membrane and a corresponding, opposite point on the second side of the osmotic membrane.
  • transmembrane osmotic pressure gradients would be determined between points 150 A and 152 A, between points 150 B and 152 B, between points 150 C and 152 C, between points 150 D and 152 D, between points 150 E and 152 E, and at a statistically representative number of point pairs across facial area 163 until a 2-dimensional profile of the transmembrane osmotic pressure gradient is produced.
  • the spatially-averaged transmembrane osmotic pressure gradient across facial area 163 of membrane 102 would then be calculated by number averaging the transmembrane osmotic pressure gradients at each point within the 2-dimensional profile.
  • the transmembrane osmotic pressure gradient, spatially-averaged across the facial area of the membrane, for one or more of the osmotic membranes within the system is less than about 45 bar, less than about 40 bar, less than about 35 bar, less than about 30 bar, less than about 25 bar, less than about 20 bar, or less (and/or, in some embodiments, at least about 1 bar, at least about 2 bar, at least about 5 bar, at least about 10 bar, or more).
  • Achieving a relatively low spatially-averaged transmembrane osmotic pressure gradient across a facial area of an osmotic membrane can be achieved, for example, by controlling the osmotic pressure of the streams fed to either side of the osmotic membrane (e.g., by controlling salt types and/or salt concentrations within the streams).
  • the difference between the osmotic pressure within the aqueous feed stream and the osmotic pressure within the first draw product stream is less than about 45 bar, less than about 40 bar, less than about 35 bar, less than about 30 bar, less than about 25 bar, less than about 20 bar, or less (and/or, in some embodiments, at least about 1 bar, at least about 2 bar, at least about 5 bar, at least about 10 bar, or more).
  • the difference between the osmotic pressure of the first draw product stream and the osmotic pressure of the second draw product stream is less than about 45 bar, less than about 40 bar, less than about 35 bar, less than about 30 bar, less than about 25 bar, less than about 20 bar, or less (and/or, in some embodiments, at least about 1 bar, at least about 2 bar, at least about 5 bar, at least about 10 bar, or more).
  • the difference between the osmotic pressure of the second draw product stream and the osmotic pressure of the third draw product stream is less than about 45 bar, less than about 40 bar, less than about 35 bar, less than about 30 bar, less than about 25 bar, less than about 20 bar, or less (and/or, in some embodiments, at least about 1 bar, at least about 2 bar, at least about 5 bar, at least about 10 bar, or more).
  • the transmembrane net driving forces from one osmotic membrane to another within the desalination system are relatively closely matched in magnitude.
  • the use of similar transmembrane net driving forces from one osmotic membrane to another within the desalination system can allow one, according to certain embodiments, to perform desalination using applied pressures that are relatively closely matched in magnitude from membrane to membrane.
  • the difference between the osmotic pressure of the first draw product stream and the osmotic pressure of the second draw inlet stream and the difference between the osmotic pressure of the second draw product stream and the osmotic pressure of the third draw inlet stream are within about 20%, within about 10%, within about 5%, within about 2%, or within about 1% of each other.
  • the difference between the osmotic pressure of the first draw product stream and the osmotic pressure of the second draw inlet stream and the difference between the osmotic pressure of the second draw product stream and the osmotic pressure of the third draw inlet stream are within about 20%, within about 10%, within about 5%, within about 2%, or within about 1% of each other.
  • first draw product stream 212 can have an osmotic pressure ( ⁇ 212 ) and second draw inlet stream 222 can have an osmotic pressure ( ⁇ 212 ), such that the difference between the osmotic pressure within the first draw product stream and the osmotic pressure of the second draw inlet stream is calculated as ⁇ 212 ⁇ 222 .
  • second draw product stream 224 can have an osmotic pressure ( ⁇ 224 ) and third draw inlet stream 234 can have an osmotic pressure ( ⁇ 234 ), such that the difference between the osmotic pressure within the second draw product stream and the osmotic pressure of the third draw inlet stream is calculated as ⁇ 224 ⁇ 234 .
  • the difference between the osmotic pressure within the first draw product stream and the osmotic pressure of the second draw inlet stream ( ⁇ 212 ⁇ 222 ) and the difference between the osmotic pressure within the second draw product stream and the osmotic pressure of the third draw inlet stream ( ⁇ 224 ⁇ 234 ) are within about 20%, within about 10%, within about 5%, within about 2%, or within about 1% of each other.
  • the difference between the osmotic pressure of the second draw product stream and the osmotic pressure of the third draw inlet stream and the difference between the osmotic pressure of the third draw product stream and the osmotic pressure of the fourth draw inlet stream are within about 20%, within about 10%, within about 5%, within about 2%, or within about 1% of each other.
  • the difference between the osmotic pressure of the second draw product stream and the osmotic pressure of the third draw inlet stream and the difference between the osmotic pressure of the third draw product stream and the osmotic pressure of the fourth draw inlet stream are within about 20%, within about 10%, within about 5%, within about 2%, or within about 1% of each other.
  • second draw product stream 224 can have an osmotic pressure ( ⁇ 224 ) and third draw inlet stream 234 can have an osmotic pressure ( ⁇ 234 ), such that the difference between the osmotic pressure within the second draw product stream and the osmotic pressure of the third draw inlet stream is calculated as ⁇ 224 ⁇ 234 .
  • third draw product stream 236 can have an osmotic pressure ( ⁇ 236 ) and fourth draw inlet stream 246 can have an osmotic pressure ( ⁇ 246 ), such that the difference between the osmotic pressure within the third draw product stream and the osmotic pressure of the fourth draw inlet stream is calculated as ⁇ 236 ⁇ 246 .
  • the difference between the osmotic pressure of the second draw product stream and the osmotic pressure of the third draw inlet stream ( ⁇ 224 ⁇ 234 ) and the difference between the osmotic pressure within the third draw product stream and the osmotic pressure of the fourth draw inlet stream ( ⁇ 236 ⁇ 246 ) are within about 20%, within about 10%, within about 5%, within about 2%, or within about 1% of each other.
  • the spatially-averaged transmembrane net driving force across the facial area of the second osmotic membrane and the spatially-averaged transmembrane net driving force across the facial area of the third osmotic membrane are within about 10%, within about 5%, within about 2%, or within about 1% of each other. In some embodiments, the spatially-averaged transmembrane net driving force across the facial area of the third osmotic membrane and the spatially-averaged transmembrane net driving force across the facial area of the fourth osmotic membrane are within about 10%, within about 5%, within about 2%, or within about 1% of each other.
  • V % Diff V 1 / V 2
  • V % ⁇ Diff V 2 - V 1 V 2 ⁇ 100 ⁇ % [ 5 ] and the first and second values would be said to be within X % of each other if V % Diff is X % or less.
  • ⁇ % ⁇ Diff ⁇ ⁇ ⁇ ⁇ 2 - ⁇ ⁇ ⁇ ⁇ 1 ⁇ ⁇ ⁇ ⁇ 2 ⁇ 100 ⁇ % [ 5 ⁇ A ] and the first and second osmotic pressure differences would be said to be within X % of each other if ⁇ % Diff is X % or less.
  • At least a portion of the energy used to pressurize one or more streams is recovered from the system.
  • the recovered energy may be used, for example, to heat and/or pressurize another stream within the desalination system.
  • Some embodiments comprise, after transporting at least a portion of the first draw product stream from the second side of the first osmotic membrane across a first side of a second osmotic membrane, reducing a pressure of the portion of the first draw product stream transported across the first side of the second osmotic membrane.
  • the pressure of second concentrated aqueous stream 226 can be reduced.
  • the pressure of the portion of the second draw product stream transported across the first side of the third osmotic membrane is reduced.
  • the pressure of third aqueous concentrated stream 238 can be reduced.
  • the pressure of the portion of the third draw product stream transported across the first side of the fourth osmotic membrane is reduced.
  • the pressure of fourth concentrated aqueous stream 250 can be reduced.
  • Some embodiments comprise recovering at least a portion of the energy released by the reduction of the pressure of a stream that exits a retentate side of an osmotic membrane (e.g., any of the concentrated aqueous streams described elsewhere herein). For example, referring to FIGS. 2A-2B , some embodiments comprise recovering at least a portion of the energy released by the reduction of the pressure of concentrated aqueous stream 214 , which exits first side 204 of osmotic membrane 202 (which is the retentate side of osmotic membrane 202 ), such as when first osmotic membrane 202 is used to perform pressure-assisted forward osmosis or reverse osmosis.
  • certain embodiments comprise recovering at least a portion of the energy released by the reduction of the pressure of concentrated aqueous stream 226 , which exits first side 218 of second osmotic membrane 216 (which is the retentate side of osmotic membrane 216 ).
  • some embodiments comprise recovering at least a portion of the energy released by the reduction of pressure of third concentrated aqueous stream 238 , which exits first side 230 of third osmotic membrane 228 (which is the retentate side of osmotic membrane 228 ).
  • Some embodiments comprise recovering at least a portion of the energy released by the reduction of pressure of concentrated aqueous stream 250 which exits first side 242 of osmotic membrane 240 (which is the retentate side of osmotic membrane 240 ).
  • Certain embodiments comprise recovering at least a portion of the energy released by the reduction of the pressure of a draw product stream that has been transported across the retentate (first) side of an osmotic membrane.
  • the recovered energy may be used to increase the pressure of another stream in the system, which can reduce overall energy costs within the system.
  • the recovered energy can be used, according to certain embodiments, to increase the pressure of a draw product stream before the draw product stream is transported across an osmotic membrane (e.g., after the draw product stream has been transported across the permeate side of an osmotic membrane, and before the draw product stream is transported across the retentate side of an osmotic membrane).
  • Some embodiments comprise recovering at least a portion of the energy released by the reduction of the pressure of the portion of the first draw product stream transported across the first side of the second osmotic membrane. In some such embodiments, at least a portion of the recovered energy is used to increase the pressure of the portion of the first draw product stream transported across the first side of the second osmotic membrane, before the portion of the first draw product stream is transported across the first side of the second osmotic membrane. For example, referring to FIG. 2B , in some embodiments, at least a portion of the energy released by reducing the pressure of second concentrated aqueous stream 226 (which includes the portion of first draw product stream 212 transported across first side 218 of second osmotic membrane 216 ) is recovered. In some such embodiments, at least a portion of the recovered energy is used to increase the pressure of at least a portion of first draw product stream 212 before it is transported across first side 218 of second osmotic membrane 216 .
  • Some embodiments comprise recovering at least a portion of the energy released by the reduction of the pressure of the portion of the second draw product stream transported across the first side of the third osmotic membrane. In some such embodiments, at least a portion of the recovered energy is used to increase the pressure of the portion of the second draw product stream transported across the first side of the third osmotic membrane, before the portion of the second draw product stream is transported across the first side of the third osmotic membrane. For example, referring to FIG. 2B , in some embodiments, at least a portion of the energy released by reducing the pressure of third concentrated aqueous stream 238 (which includes the portion of second draw product stream 224 transported across first side 230 of third osmotic membrane 228 ) is recovered. In some such embodiments, at least a portion of the recovered energy is used to increase the pressure of at least a portion of second draw product stream 224 before it is transported across first side 230 of third osmotic membrane 228 .
  • Some embodiments comprise recovering at least a portion of the energy released by the reduction of the pressure of the portion of the third draw product stream transported across the first side of the fourth osmotic membrane. In some such embodiments, at least a portion of the recovered energy is used to increase the pressure of the portion of the third draw product stream transported across the first side of the fourth osmotic membrane, before the portion of the third draw product stream is transported across the first side of the fourth osmotic membrane. For example, referring to FIG. 2B , in some embodiments, at least a portion of the energy released by reducing the pressure of fourth concentrated aqueous stream 250 (which includes the portion of third draw product stream 236 transported across first side 242 of fourth osmotic membrane 240 ) is recovered. In some such embodiments, at least a portion of the recovered energy is used to increase the pressure of at least a portion of third draw product stream 236 before it is transported across first side 242 of fourth osmotic membrane 240 .
  • Certain embodiments comprise recovering at least a portion of the energy released by the reduction of the pressure of a stream that exits a retentate side of an upstream osmotic membrane, and at least a portion of the energy that is recovered can be used to increase the pressure of a stream that is transported across the retentate side of a downstream osmotic membrane (i.e., an osmotic membrane that is downstream of the upstream osmotic membrane).
  • at least a portion of the energy recovered via the reduction of the pressure of the stream that exits the retentate side of the upstream osmotic membrane can be used to increase the pressure of a stream that exits the permeate side of the upstream osmotic membrane.
  • at least a portion of the stream that exits the permeate side of the upstream osmotic membrane can then be transferred across the retentate side of a downstream osmotic membrane.
  • Certain embodiments comprise recovering at least a portion of the energy released by reducing the pressure of the first concentrated aqueous stream that exits the first side of the first osmotic membrane.
  • at least a portion of the recovered energy is used to increase the pressure of at least a portion of the first draw product stream before it is transported across the first side of the second osmotic membrane.
  • At least a portion, or all, of the first draw product stream may originate, for example, from the permeate side of the first osmotic membrane.
  • at least a portion of the energy released by reducing the pressure of concentrated aqueous stream 214 is recovered.
  • At least a portion of the recovered energy is used to increase the pressure of at least a portion of first draw product stream 212 (which originates from second side 206 (the permeate side) of first osmotic membrane 202 ) before it is transported across first side 218 of second osmotic membrane 216 .
  • Some embodiments comprise recovering at least a portion of the energy released by reducing the pressure of the second concentrated aqueous stream that exits the first side of the second osmotic membrane.
  • at least a portion of the recovered energy is used to increase the pressure of at least a portion of the second draw product stream before it is transported across the first side of the third osmotic membrane.
  • At least a portion, or all, of the second draw product stream may originate, for example, from the permeate side of the second osmotic membrane.
  • at least a portion of the energy released by reducing the pressure of second concentrated aqueous stream 226 is recovered.
  • At least a portion of the recovered energy is used to increase the pressure of at least a portion of second draw product stream 224 (which originates from second side 220 (the permeate side) of second osmotic membrane 216 ) before it is transported across first side 230 of third osmotic membrane 228 .
  • Certain embodiments comprise recovering at least a portion of the energy released by reducing the pressure of the third concentrated aqueous stream that exits the first side of the third osmotic membrane.
  • at least a portion of the recovered energy is used to increase the pressure of at least a portion of the third draw product stream before it is transported across the first side of the fourth osmotic membrane.
  • At least a portion, or all, of the third draw product stream may originate, for example, from the permeate side of the third osmotic membrane.
  • at least a portion of the energy released by reducing the pressure of third concentrated aqueous stream 238 is recovered.
  • At least a portion of the recovered energy is used to increase the pressure of at least a portion of third draw product stream 236 (which originates from second side 232 (which is the permeate side) of third osmotic membrane 228 ) before it is transported across first side 242 of fourth osmotic membrane 240 .
  • combinations of the energy recovery methods described above can be employed.
  • some embodiments comprise recovering at least a portion of the energy released by the reduction of the pressure of a stream that exits a retentate side of an upstream osmotic membrane and recovering at least a portion of energy released by the reduction of the pressure of a stream that exits a retentate side of a downstream osmotic membrane (i.e., an osmotic membrane that is downstream of the upstream osmotic membrane).
  • At least a portion of the energy recovered from the reduction of the pressure of the stream that exits the retentate side of the upstream osmotic membrane and at least a portion of the energy recovered from the reduction of the pressure of the stream that exits the retentate side of the downstream osmotic membrane are used to increase the pressure of another stream in the system (e.g., to increase the pressure of the stream that exits the permeate side of the upstream osmotic membrane and/or to increase the pressure of the stream that enters the retentate side of the downstream osmotic membrane).
  • some embodiments comprise (1) recovering at least a portion of the energy released by the reduction of the pressure of concentrated aqueous stream 238 which exits first side 230 (which is the retentate side) of third osmotic membrane 228 (which is upstream of fourth osmotic membrane 240 ) and (2) recovering at least a portion of energy released by the reduction of the pressure of concentrated aqueous stream 250 which exits first side 242 (which is the retentate side) of osmotic membrane 240 (which is downstream of third osmotic membrane 228 ).
  • At least a portion of the energy recovered from the reduction of the pressure of concentrated aqueous stream 238 and at least a portion of the energy recovered from the reduction of the pressure of concentrated aqueous stream 250 are used to increase the pressure of third draw product stream 236 , which exits second side 228 of third osmotic membrane and/or to increase the pressure of the portion of third draw product stream 236 that is transported across first side 242 of fourth osmotic membrane 240 before the portion of third draw product stream 236 is transported across first side 242 of fourth osmotic membrane 240 .
  • a first pressure exchange device can be used to transfer energy from stream 238 to stream 236
  • a second pressure exchange device can be used to transfer energy from stream 250 to stream 236 .
  • fourth osmotic membrane 240 is not present (as it is an optional feature). Some embodiments comprise (1) recovering at least a portion of the energy released by the reduction of the pressure of concentrated aqueous stream 226 which exits first side 218 (which is the retentate side) of second osmotic membrane 216 (which is upstream of third osmotic membrane 228 ) and (2) recovering at least a portion of energy released by the reduction of the pressure of concentrated aqueous stream 238 which exits first side 230 (which is the retentate side) of third osmotic membrane 228 (which is downstream of second osmotic membrane 216 ).
  • At least a portion of the energy recovered from the reduction of the pressure of concentrated aqueous stream 226 and at least a portion of the energy recovered from the reduction of the pressure of concentrated aqueous stream 238 are used to increase the pressure of second draw product stream 224 , which exits second side 220 of second osmotic membrane 216 and/or to increase the pressure of the portion of second draw product stream 224 that is transported across first side 218 of third osmotic membrane 228 before the portion of second draw product stream 224 is transported across first side 230 of third osmotic membrane 228 .
  • a first pressure exchange device can be used to transfer energy from stream 226 to stream 224
  • a second pressure exchange device can be used to transfer energy from stream 238 to stream 224 .
  • the recovery of energy from multiple streams can be used to pressurize a stream that is transported to the retentate side of the final osmotic membrane in a series of osmotic membranes.
  • the “final” osmotic membrane in this context, refers to the osmotic membrane that produces the final aqueous product, and after which, no additional osmosis steps are performed. Referring to FIG.
  • fourth osmotic membrane 240 can be the final osmotic membrane in a series of osmotic membranes.
  • third osmotic membrane may be the penultimate osmotic membrane in a series of osmotic membranes.
  • one or more intermediate osmotic membranes can be positioned between second osmotic membrane 216 and third osmotic membrane 228 within the series of osmotic membranes.
  • energy is recovered by reducing the pressure of concentrated aqueous stream 238 and by reducing the pressure of concentrated aqueous stream 250 , and at least portions of the energies recovered from the reduction of the pressure of concentrated aqueous stream 238 and concentrated aqueous stream 250 are used to increase the pressure of third draw product stream 236 (e.g., as it exits second side 232 of third osmotic membrane 228 and/or before it is fed to first side 242 of fourth osmotic membrane 240 ).
  • fourth draw product stream 248 forms all or part of a final product stream (e.g., purified water), and, in some such cases, no further osmosis steps are performed on stream 248 .
  • fourth osmotic membrane is absent.
  • third osmotic membrane 228 can be the final osmotic membrane in a series of osmotic membranes.
  • second osmotic membrane 216 may be the penultimate osmotic membrane in a series of osmotic membranes.
  • energy is recovered by reducing the pressure of concentrated aqueous stream 226 and by reducing the pressure of concentrated aqueous stream 238 , and at least portions of the energies recovered from the reduction of the pressure of concentrated aqueous stream 226 and concentrated aqueous stream 238 are used to increase the pressure of second draw product stream 224 (e.g., as it exits second side 220 of second osmotic membrane 216 and/or before it is fed to first side 230 of third osmotic membrane 228 ).
  • third draw product stream 236 forms all or part of a final product stream (e.g., purified water), and, in some such cases, no further osmosis steps are performed on stream 236 .
  • Energy from a pressurized stream can be recovered via any suitable method.
  • a pressure exchange device can be used to recover energy from a pressurized stream.
  • Those of ordinary skill in the art are familiar with pressure exchange devices, in which pressure energy from a high pressure fluid stream is transferred to a low pressure fluid stream.
  • An exemplary type of pressure exchange device is a rotary pressure exchanger, for example, as described in U.S. Pat. No. 7,306,437.
  • energy e.g., as direct hydraulic pressure
  • energy can be recovered by directly contacting a pressurized stream with a stream at a lower pressure, such that the lower pressure stream is pressurized and the higher pressure stream is depressurized (e.g., throttled).
  • Energy can also be recovered in the system using other devices such as, for example, a turbine (e.g., a Pelton wheel).
  • the stream fed to the desalination system is an aqueous stream comprising at least one solubilized ion species.
  • aqueous feed stream 208 can comprise an aqueous stream comprising at least one solubilized ion species.
  • the solubilized ion(s) may originate, for example, from a salt that has been dissolved in the aqueous stream.
  • a solubilized ion is generally an ion that has been solubilized to such an extent that the ion is no longer ionically bonded to a counter-ion.
  • the aqueous feed stream can comprise any of a number of solubilized ion species including, but not limited to, Na + , Mg 2+ , Ca 2+ , Sr 2+ , Ba 2+ , Cl ⁇ , carbonate anions, bicarbonate anions, sulfate anions, bisulfate anions, and/or dissolved silica.
  • the aqueous feed stream comprises at least one solubilized monovalent cation (i.e., a cation with a redox state of +1 when solubilized).
  • the aqueous feed stream comprises Na + and/or K + .
  • the aqueous feed stream comprises at least one monovalent anion (i.e., an anion having redox state of ⁇ 1 when solubilized).
  • the aqueous feed stream comprises Cl ⁇ and/or Br ⁇ .
  • the aqueous feed stream comprises at least one monovalent cation and at least one monovalent anion.
  • the aqueous feed stream comprises one or more divalent cations (i.e., a cation with a redox state of +2 when solubilized) and/or one or more divalent anions (i.e., an anion with a redox state of ⁇ 2 when solubilized). Cations and/or anions having other valencies may also be present in the aqueous feed stream, in some embodiments.
  • the total concentration of solubilized ions in the aqueous feed stream fed to the first osmotic membrane can be relatively high.
  • one advantage associated with certain embodiments is that initial aqueous feed streams with relatively high solubilized ion concentrations can be desalinated without the use of energy intensive desalination methods.
  • the total concentration of solubilized ions in the aqueous feed stream transported to the first osmotic membrane is at least about 60,000 ppm, at least about 80,000 ppm, or at least about 100,000 ppm (and/or, in some embodiments, up to about 500,000 ppm, or more).
  • Aqueous feed streams with solubilized ion concentrations outside these ranges could also be used.
  • the aqueous feed stream that is transported to the first osmotic membrane comprises a suspended and/or emulsified immiscible phase.
  • a suspended and/or emulsified immiscible phase is a material that is not soluble in water to a level of more than 10% by weight at the temperature and other conditions at which the stream is operated.
  • the suspended and/or emulsified immiscible phase comprises oil and/or grease.
  • oil generally refers to a fluid that is more hydrophobic than water and is not miscible or soluble in water, as is known in the art.
  • the oil may be a hydrocarbon in some embodiments, but in other embodiments, the oil may comprise other hydrophobic fluids.
  • At least about 0.1 wt %, at least about 1 wt %, at least about 2 wt %, at least about 5 wt %, or at least about 10 wt % (and/or, in some embodiments, up to about 20 wt %, up to about 30 wt %, up to about 40 wt %, up to about 50 wt %, or more) of the aqueous feed stream is made up of a suspended and/or emulsified immiscible phase.
  • the first osmotic membrane is configured such that little or none of the suspended and/or emulsified immiscible phase is transported through the first osmotic membrane.
  • the first osmotic membrane is configured such that little or none of the suspended and/or emulsified immiscible phase is transported through the first osmotic membrane.
  • less than about 10 wt %, less than about 5 wt %, less than about 2 wt %, less than about 1 wt %, or substantially none of the suspended and/or emulsified immiscible phase is transported through the first osmotic membrane as the aqueous feed stream is transported across the first osmotic membrane.
  • the first osmotic membrane can be used to separate a suspended and/or emulsified immiscible phase from an incoming aqueous feed stream, such separation is optional.
  • the aqueous feed stream transported to the desalination system is substantially free of a suspended and/or emulsified immiscible phase.
  • one or more separation units upstream of the first osmotic membrane can be used to at least partially remove a suspended and/or emulsified immiscible phase from an aqueous feed stream before the aqueous feed stream is transported to the first osmotic membrane.
  • Non-limiting examples of such systems are described, for example, in International Patent Publication No. WO 2015/021062, published on Feb. 12, 2015, which is incorporated herein by reference in its entirety for all purposes.
  • the aqueous feed stream can be derived from seawater, ground water, brackish water, and/or the effluent of a chemical process.
  • aqueous feed stream that may be encountered is produced water (e.g., water that emerges from oil or gas wells along with the oil or gas). Due to the length of time produced water has spent in the ground, and due to high subterranean pressures and temperatures that may increase the solubility of certain salts and minerals, produced water often comprises relatively high concentrations of dissolved salts and minerals.
  • some produced water streams may comprise a supersaturated solution of dissolved strontium sulfate (SrSO 4 ).
  • flowback water e.g., water that is injected as a fracking fluid during hydraulic fracturing operations and subsequently recovered.
  • Flowback water often comprises a variety of constituents used in fracking, including surfactants, proppants, and viscosity reducing agents, but often has a lower salinity than produced water.
  • the systems and methods described herein can be used to at least partially desalinate aqueous feed streams derived from such process streams.
  • the first draw inlet stream (e.g., stream 210 in FIGS. 2A-2B ) can comprise, according to certain embodiments, any component(s) suitable for imparting an appropriate osmotic pressure to perform the functions described herein.
  • the first draw inlet stream is an aqueous solution comprising one or more solubilized species, such as one or more dissolved ions and/or one or more dissociated molecules.
  • the first draw inlet stream comprises Na + , Mg 2+ , Ca 2+ , Sr 2+ , Ba 2+ , and/or Cl ⁇ .
  • the first draw inlet stream comprises at least one solubilized monovalent cation, such as Na + and/or K + .
  • the first draw inlet stream comprises at least one monovalent anion, such as Cl ⁇ and/or Br ⁇ . Cations and/or anions having other valencies may also be present in the first draw inlet stream. Other species could also be used in the draw stream.
  • the first draw inlet stream can be an aqueous stream comprising a solubilized non-ionic species, such as ammonia (NH 3 ).
  • the second draw inlet stream (e.g., stream 222 in FIGS. 2A-2B ) can also comprise any component(s) suitable for imparting an appropriate osmotic pressure to perform the functions described herein, according to certain embodiments.
  • the second draw inlet stream is an aqueous solution comprising one or more solubilized species, such as one or more dissolved ions and/or one or more dissociated molecules.
  • the second draw inlet stream comprises Na + , Mg 2+ , Ca 2+ , Sr 2+, Ba 2+ , and/or Cl ⁇ .
  • the second draw inlet stream comprises at least one solubilized monovalent cation, such as Na + and/or K + .
  • the second draw inlet stream comprises at least one monovalent anion, such as Cl ⁇ and/or Br ⁇ . Cations and/or anions having other valencies may also be present in the second draw inlet stream. Other species could also be used in the second draw inlet stream.
  • the second draw inlet stream can be an aqueous stream comprising a solubilized non-ionic species, such as ammonia (NH 3 ).
  • the second draw inlet stream can included solubilized species (e.g., solubilized ion species) that are the same as or different from those present in the first draw inlet stream.
  • the total molar concentration (in units of molarity) of solubilized species (e.g., solubilized ions) in the second draw inlet stream is lower than the total molar concentration of solubilized species (e.g., solubilized ions) in the first draw inlet stream.
  • the third draw inlet stream (e.g., stream 234 in FIG. 2B ) can also, according to certain embodiments, comprise any component(s) suitable for imparting an appropriate osmotic pressure to perform the functions described herein.
  • the third draw inlet stream is an aqueous solution comprising one or more solubilized species, such as one or more ions and/or one or more dissociated molecules.
  • the third draw inlet stream comprises Na + , Mg 2+ , Ca 2+ , Sr 2+ , Ba 2+ , and/or Cl ⁇ .
  • the third draw inlet stream comprises at least one solubilized monovalent cation, such as Na + and/or K + .
  • the third draw inlet stream comprises at least one monovalent anion, such as Cl ⁇ and/or Br ⁇ . Cations and/or anions having other valencies may also be present in the third draw inlet stream. Other species could also be used in the third draw inlet stream.
  • the third draw inlet stream can be an aqueous stream comprising a solubilized a non-ionic species, such as ammonia (NH 3 ).
  • the third draw inlet stream can included solubilized species (e.g., solubilized ions) that are the same as or different from those present in the first and/or second draw inlet stream.
  • the total molar concentration of solubilized species (e.g., solubilized ions) in the third draw inlet stream is lower than the total molar concentration of solubilized species (e.g., solubilized) ions in the second draw inlet stream.
  • the fourth draw inlet stream (e.g., stream 246 in FIG. 2B ) can also comprise any component(s) suitable for imparting an appropriate osmotic pressure to perform the functions described herein, according to certain embodiments.
  • the fourth draw inlet stream is an aqueous solution comprising one or more solubilized species, such as one or more dissolved ions and/or one or more dissociated molecules.
  • the fourth draw inlet stream comprises Na + , Mg 2+ , Ca 2+ , Sr 2+ , Ba 2+ , and/or Cl ⁇ .
  • the fourth draw inlet stream comprises at least one solubilized monovalent cation, such as Na + and/or K + .
  • the fourth draw inlet stream comprises at least one monovalent anion, such as Cl ⁇ and/or Br ⁇ . Cations and/or anions having other valencies may also be present in the fourth draw inlet stream. Other species could also be used in the fourth draw inlet stream.
  • the fourth draw inlet stream is an aqueous stream comprising a solubilized non-ionic species, such as ammonia (NH 3 ).
  • the fourth draw inlet stream can include solubilized ion species that are the same as or different from those present in the first, second, and/or third draw inlet streams.
  • the total molar concentration of solubilized species (e.g., solubilized ions) in the fourth draw inlet stream is lower than the total molar concentration of solubilized species (e.g., solubilized ions) in the third draw inlet stream.
  • the draw inlet streams may be prepared, according to certain embodiments, by suspending and/or dissolving one or more species in a solvent, such as an aqueous solvent) to solubilize the species in the solvent.
  • a solvent such as an aqueous solvent
  • one or more draw inlet streams can be made by dissolving one or more solid salts in an aqueous solvent.
  • salts that may be dissolved in water include NaCl, CaCl 2 , MgCl 2 , and the like.
  • the draw stream can be prepared by mixing ammonia with water.
  • the draw stream can be prepared by dissolving one or more ammonia salts (e.g., ammonium bicarbonate, ammonium carbonate, and/or ammonium carbamate) in water.
  • the draw stream can be prepared by dissolving ammonia and carbon dioxide gasses in water.
  • the membrane medium can comprise, for example, a metal, a ceramic, a polymer (e.g., polyamides, polyethylenes, polyesters, poly(tetrafluoroethylene), polysulfones, polycarbonates, polypropylenes, poly(acrylates)), and/or composites or other combinations of these.
  • Osmotic membranes generally allow for the selective transport of water through the membrane, in which water is capable of being transmitted through the membrane while solubilized species (e.g., ions) are inhibited from being transported through the membrane.
  • osmotic membranes examples include, but are not limited to, those commercially available from Dow Water and Process Solutions (e.g., FilmTecTM membranes), Hydranautics, GE Osmonics, and Toray Membrane, among others known to those of ordinary skill in the art.
  • a single stage osmotic membrane system which is used to perform draw-assisted reverse osmosis.
  • the system contained a single nonporous membrane with a feed side, across which a pressurized influent feed stream flowed, and a draw side, across which an influent draw stream flowed.
  • the systems was operated as follows, with reference to the exemplary diagram shown in FIG. 1A .
  • the system comprised an osmotic membrane 102 with a first side 104 and a second side 106 .
  • An influent aqueous feed stream 108 was transported across the first side 104
  • an influent draw stream 110 was transported across the second side 106 .
  • Water was transported between the first side 104 and second side 106 of the osmotic membrane 102 to produce an aqueous stream 114 , from the influent aqueous feed stream 108 , and a draw product stream 112 , from the draw stream 110 .
  • the osmotic membrane 102 in this system was manufactured by Porifera, and had a total area of 1 m 2 comprising a nonporous active layer on the first side 104 and a porous nonwoven structural support layer on the second side 106 .
  • the osmotic membrane was contained inside a counter-current plate and frame module, also manufactured by Porifera.
  • Aqueous feed stream 108 and draw stream 110 were prepared by dissolving Sonoma sea salt in deionized water.
  • Aqueous feed stream 108 was pumped from a first vessel across the first side 104 of osmotic membrane 102 by a first diaphragm pump.
  • the hydraulic pressure on the first side 104 was controlled by a Swagelok backpressure regulator at the outlet of the membrane module through which effluent aqueous stream 114 flowed.
  • the aqueous stream 114 was collected in a second vessel.
  • Draw stream 110 was pumped from a third vessel across the second side of osmotic membrane 102 by a second diaphragm pump.
  • the effluent draw product stream 112 was collected in a fourth vessel.
  • Pressure was measured by dial indicators at the osmotic membrane module outlet through which the effluent aqueous stream 114 flowed and at the osmotic membrane module outlet through which the effluent draw product stream 112 flowed.
  • Transmembrane pressure was calculated as the difference between the pressure measured at these locations.
  • Flow rates of the influent aqueous feed stream 108 , of the effluent aqueous stream 114 , of the influent draw stream 110 , and of the effluent draw product stream 112 were measured gravimetrically by weighing the first, second, third and fourth vessel respectively at intervals of 10-15 minutes. The weight changes and interval between the weighings of each vessel were used to calculate the mass flow rate of each stream. Difference between the mass flow rate of aqueous feed stream 108 and aqueous stream 114 , and the difference between the mass flow rate of draw stream 110 and draw product stream 112 were averaged to calculate the flux across the osmotic membrane 102 .
  • Sodium concentration of each stream was analyzed using an inductively coupled plasma optical emission spectrometer manufactured by Perkin Elmer from samples collected from each of the four vessels at increments of 10-15 minutes.
  • the salinity of the draw stream source was varied and the effect of the variation on transmembrane flux was measured.
  • the osmotic membrane system was allowed to reach a steady state by operating for one hour at fixed conditions before flow rate, pressure, and salinity measurements were taken.
  • a source of aqueous feed stream 108 was prepared and measured to contain 1900 mg/L sodium.
  • the transmembrane pressure was adjusted to 17 psi.
  • the flow rate of the aqueous feed stream 108 was 45.77 ml/min, and the flow rate of the draw stream 110 was 39.28.
  • the salinity of the draw stream source and the resulting transmembrane flux is shown in Table 1.
  • the flux is shown to reverse direction between trials 1 and 2, and increase further in trial 3.
  • the transmembrane pressure was not sufficient to overcome the osmotic pressure difference across the membrane 102 , so water flowed across the osmotic membrane 102 from the second side 106 to the first side 104 .
  • the salinity of the draw stream 110 reduced the osmotic pressure difference between the two sides.
  • the salinity of the feed stream 108 was greater than the salinity of the draw stream 110 , the resulting osmotic pressure difference was not sufficient to overcome the transmembrane pressure, resulting in a positive flux from the first side 104 to the second side 106 .
  • the osmotic pressure difference is further reduced by the increased salinity of the draw stream 110 , resulting in a greater positive flux.
  • a multistaged osmotic membrane cascade was simulated by repeated experiments on a single osmotic membrane system in which the draw stream product from previous trials was used as the feed stream for each trial after the first.
  • the systems was operated as follows, with reference to the exemplary diagram shown in FIG. 1A .
  • the system comprised an osmotic membrane 102 with a first side 104 and a second side 106 .
  • An influent aqueous feed stream 108 was transported across the first side 104
  • an influent draw stream 110 was transported across the second side 106 .
  • Water was transported between the first side 104 and second side 106 of the osmotic membrane 102 to produce an aqueous stream 114 , from the influent aqueous feed stream 108 , and a draw product stream 112 , from the draw stream 110 .
  • the osmotic membrane 102 in this system was manufactured by Porifera, and had a total area of 1 m 2 comprising a nonporous active layer on the first side 104 and a porous nonwoven structural support layer on the second side 106 .
  • the osmotic membrane was contained inside a counter-current plate and frame module, also manufactured by Porifera.
  • Aqueous feed stream 108 and draw stream 110 were prepared by dissolving Sonoma sea salt in deionized water.
  • Aqueous feed stream 108 was pumped from a first vessel across the first side 104 of osmotic membrane 102 by a first diaphragm pump.
  • the hydraulic pressure on the first side 104 was controlled by a Swagelok backpressure regulator at the outlet of the membrane module through which effluent aqueous stream 114 flowed.
  • the aqueous stream 114 was collected in a second vessel.
  • Draw stream 110 was pumped from a third vessel across the second side of osmotic membrane 102 by a second diaphragm pump.
  • the effluent draw product stream 112 was collected in a fourth vessel.
  • Pressure was measured by dial indicators at the osmotic membrane module outlet through which the effluent aqueous stream 114 flowed and at the osmotic membrane module outlet through which the effluent draw product stream 112 flowed.
  • Transmembrane pressure was calculated as the difference between the pressure measured at these locations.
  • Flow rates of the influent aqueous feed stream 108 , of the effluent aqueous stream 114 , of the influent draw stream 110 , and of the effluent draw product stream 112 were measured gravimetrically by weighing the first, second, third and fourth vessel respectively at intervals of 10-15 minutes. The weight changes and interval between the weighings of each vessel were used to calculate the mass flow rate of each stream.
  • the difference between the mass flow rate of aqueous feed stream 108 and aqueous stream 114 , and the difference between the mass flow rate of draw stream 110 and draw product stream 112 were averaged to calculate the flux across the osmotic membrane 102 .
  • the sodium concentration of each stream was analyzed using an inductively coupled plasma optical emission spectrometer manufactured by Perkin Elmer from samples collected from each of the four vessels at increments of 10-15 minutes.
  • the salinity of the aqueous feed stream 108 and the draw stream 110 were varied in successive trials to simulate a membrane cascade.
  • a starting aqueous feed stream salinity and draw stream salinity was selected.
  • the resulting draw stream product of the first trial was collected and used as the source of the aqueous feed stream 108 in the second trial.
  • the resulting draw product stream of the second trial was collected and used as the source of the aqueous feed stream 108 in the third trial.
  • the resulting draw product stream of the third trial was collected and used as the source of the aqueous feed stream 108 in the fourth trial.
  • first draw product stream 212 flowing from a first osmotic membrane 202 , is fed to the first side of a second osmotic membrane 216 .
  • Downstream membranes are similarly fed feed streams comprising the draw product stream resulting from upstream membranes.
  • the cascade experiment was performed for first trial feed streams of 5000 ppm and 50,000 ppm.
  • a set of single stage trials were also performed for each first trial feed salinity, in which the draw stream salinity was equal to the final draw stream salinity of the corresponding cascade experiment.
  • the results of the 5000 ppm feed stream cascade experiment and corresponding single-stage comparison experiment are displayed in Table 2.
  • the results of the 50,000 ppm feed stream experiments are displayed in Table 3.
  • This prophetic example describes a desalination system in which an initial forward osmosis process is combined with a series of downstream reverse osmosis processes to produce an aqueous product stream with a higher purity of water than the initial aqueous feed stream.
  • FIG. 3A An exemplary process is shown in the schematic diagram of FIG. 3A .
  • an aqueous feed stream including 10 wt % dissolved NaCl is transported to a first side of a first osmotic membrane.
  • An aqueous draw solution comprising 22 wt % dissolved NaCl is transported to the second side of the first osmotic membrane, in a counter-flow arrangement relative to the aqueous feed stream.
  • the first osmotic membrane is used to perform forward osmosis, such that a concentrated reject brine stream containing 20 wt % dissolved NaCl is produced and transported away from the first side of the first osmotic membrane, and a diluted draw solution containing 10.47 wt % dissolved NaCl is produced and transported away from the second side of the first osmotic membrane.
  • the diluted draw solution from the first osmotic membrane is transported, using a pump, to the first side of a second osmotic membrane.
  • An aqueous intermediate draw solution comprising 20 wt % dissolved NaCl is transported to the second side of the second osmotic membrane, in a counter-flow arrangement relative to the dilute draw solution stream.
  • a hydraulic pressure of 20 bar is applied to the first side of the second osmotic membrane, and a reverse osmosis process is performed such that a concentrated draw solution stream containing 22 wt % dissolved NaCl is produced and transported away from the first side of the second osmotic membrane, and a diluted intermediate draw solution containing 8.72 wt % dissolved NaCl is produced and transported away from the second side of the second osmotic membrane.
  • At least a portion (or all) of the recovered concentrated draw solution stream can be throttled to a desired pressure (e.g., decreasing the pressure by about 14 bar to a pressure of about 6 bar) and sent back to the first osmotic membrane in a closed or at least partially closed loop.
  • the diluted intermediate draw solution from the second osmotic membrane is transported, using a pump, to the first side of a third osmotic membrane.
  • An aqueous draw solution comprising 18 wt % dissolved NaCl is transported to the second side of the third osmotic membrane, in a counter-flow arrangement relative to the dilute intermediate draw solution stream.
  • a hydraulic pressure of 20 bar is applied to the first side of the third osmotic membrane, and a reverse osmosis process is performed such that a concentrated draw solution stream containing 20 wt % dissolved NaCl is produced and transported away from the first side of the third osmotic membrane, and a diluted intermediate draw solution containing 6.98 wt % dissolved NaCl is produced and transported away from the second side of the third osmotic membrane.
  • At least a portion (or all) of the recovered concentrated draw solution stream can be throttled to a desired pressure (e.g., decreasing the pressure by about 14 bar to a pressure of about 6 bar) and sent back to the second osmotic membrane in a closed or at least partially closed loop.
  • Third, fourth, and fifth reverse osmosis processes are also performed, such that a further diluted aqueous stream containing 1.83 wt % dissolved NaCl is produced.
  • the diluted aqueous stream containing 1.83 wt % dissolved NaCl is transported to the first side of a seventh osmotic membrane (to perform a sixth reverse osmosis process).
  • An additional draw solution containing 10 wt % of dissolved NaCl is transported to the second side of the seventh osmotic membrane.
  • a hydraulic pressure of 20 bar is applied to the first side of the seventh osmotic membrane, and a reverse osmosis process is performed such that a concentrated aqueous stream containing 12 wt % dissolved NaCl is produced and transported away from the first side of the seventh osmotic membrane, and a final product stream containing substantially pure water (about 0.15% NaCl) is produced and transported away from the second side of the seventh osmotic membrane.
  • At least a portion (or all) of the recovered concentrated draw solution stream can be throttled to a desired pressure (e.g., decreasing the pressure by about 14 bar to a pressure of about 6 bar) and sent back to the sixth osmotic membrane in a closed or at least partially closed loop.
  • This prophetic example describes the use of energy recovery in a desalination system in which an initial forward osmosis process is combined with a series of downstream reverse osmosis processes to produce an aqueous product stream with a higher purity of water than the initial aqueous feed stream.
  • FIG. 3B is a schematic illustration of an exemplary desalination system in which energy is recovered at multiple points in the system.
  • the energy can be recovered as direct hydraulic pressure, for example, using a pressure exchange device (instead of or in addition to a throttle).
  • the process illustrated in FIG. 3B includes that same four initial osmotic stages as described above with respect to FIG. 3A (with similar streams and component concentrations, and similar osmotic membranes), except energy recovery devices have been added to the embodiment shown in FIG. 3B .
  • the 22 wt % dissolved NaCl recovered draw solution from the second osmotic membrane (which is at a higher hydraulic pressure than the dilute 10.47 wt % dissolved NaCl draw solution exiting the first osmotic membrane) can be used to transfer energy (in the form of pressure) via direct contact (e.g., in a rotary pressure exchange device) with the dilute 10.47 wt % dissolved NaCl draw solution before the dilute draw solution is pressurized and sent to the second osmotic membrane.
  • the 22 wt % dissolved NaCl recovered draw solution is depressurized (throttled). While a rotary pressure exchange device is illustrated in FIG. 3B , other devices (e.g., a Pelton wheel) could also be used.
  • the 20 wt % dissolved NaCl recovered draw solution (which is at a higher hydraulic pressure than the 8.72 wt % dissolved NaCl dilute draw solution) can be used to transfer energy (in the form of pressure) via direct contact (e.g., in a rotary pressure exchange device) with the dilute 8.72 wt % dissolved NaCl draw solution before the dilute draw solution is pressurized and sent to the third osmotic membrane. During this process, the 20 wt % dissolved NaCl recovered draw solution is depressurized (throttled).
  • the 18 wt % dissolved NaCl recovered draw solution (which is at a higher hydraulic pressure than the 6.98 wt % dissolved NaCl dilute draw solution) can be used to transfer energy (in the form of pressure) via direct contact (e.g., in a rotary pressure exchange device) with the dilute 6.98 wt % dissolved NaCl draw solution before the dilute draw solution is pressurized and sent to the fourth osmotic membrane. During this process, the 18 wt % dissolved NaCl recovered draw solution is depressurized (throttled).
  • This prophetic example describes the operation of an osmotic membrane separator in which flow rates, osmotic pressures, and hydraulic pressures of inlet streams are selected to balance the net osmotic driving force across the facial area of the osmotic membrane.
  • FIG. 4A A schematic illustration of the osmotic membrane separator is shown in FIG. 4A .
  • the osmotic membrane separator comprises osmotic membrane 102 , defining a first side 104 and a second side 106 .
  • Feed stream 108 has a mass flow rate m F,i , an osmotic pressure ⁇ F,i , and a hydraulic pressure P F .
  • Concentrated aqueous stream 114 has a mass flow rate m F,o , an osmotic pressure ⁇ F,o , and a hydraulic pressure P F .
  • Draw inlet stream 110 has a mass flow rate m D,i , an osmotic pressure ⁇ D,i , and a hydraulic pressure P D .
  • Draw product stream 112 has a mass flow rate m D,o , an osmotic pressure ⁇ D,o , and a hydraulic pressure P D .
  • Feed stream 108 is transported across first side 104 of osmotic membrane 102
  • draw inlet stream 110 is transported across second side 106 of osmotic membrane 102 in a direction opposite the direction of feed stream 108 .
  • the osmotic separator is operated in a counterflow configuration.
  • FIG. 4B is a plot of osmotic pressure as a function of position across the osmotic membrane. As seen in FIG. 4B , the difference between the feed osmotic pressure and the draw osmotic pressure remains relatively constant across the osmotic membrane. In this example, the maximum net driving force and the minimum net driving force are within 9.05% of each other.
  • a reference to “A and/or B,” when used in conjunction with open-ended language such as “comprising” can refer, in one embodiment, to A without B (optionally including elements other than B); in another embodiment, to B without A (optionally including elements other than A); in yet another embodiment, to both A and B (optionally including other elements); etc.
  • the phrase “at least one,” in reference to a list of one or more elements, should be understood to mean at least one element selected from any one or more of the elements in the list of elements, but not necessarily including at least one of each and every element specifically listed within the list of elements and not excluding any combinations of elements in the list of elements.
  • This definition also allows that elements may optionally be present other than the elements specifically identified within the list of elements to which the phrase “at least one” refers, whether related or unrelated to those elements specifically identified.
  • “at least one of A and B” can refer, in one embodiment, to at least one, optionally including more than one, A, with no B present (and optionally including elements other than B); in another embodiment, to at least one, optionally including more than one, B, with no A present (and optionally including elements other than A); in yet another embodiment, to at least one, optionally including more than one, A, and at least one, optionally including more than one, B (and optionally including other elements); etc.

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Abstract

Provided herein are osmotic desalination methods and associated systems. According to certain embodiments, multiple osmotic membranes may be used to perform a series of osmosis steps, such that an output stream having a relatively high water purity—compared to a water purity of an aqueous feed stream—is produced. In some embodiments, multiple draw streams can be used to produce aqueous product streams having sequentially higher purities of water. Certain embodiments are related to osmotic desalination systems and methods in which forward osmosis is used to produce a first product stream having a relatively high water purity relative to an aqueous feed stream, and reverse osmosis is used to perform a second step (and/or additional steps) on the first product stream. In some embodiments, multiple reverse osmosis steps can be used in series to perform a net desalination process.

Description

RELATED APPLICATIONS
This application is a continuation of U.S. patent application Ser. No. 15/747,907 (issued as U.S. Pat. No. 10,518,221), filed Jan. 26, 2018, which is a U.S. National Stage patent application based on International Patent Application No. PCT/US2016/044663, filed Jul. 29, 2016, which claims priority under 35 U.S.C. § 119(e) to U.S. Provisional Patent Application Ser. No. 62/198,413, filed Jul. 29, 2015, each of which is incorporated herein by reference in its entirety for all purposes.
TECHNICAL FIELD
Osmotic desalination methods and associated systems are generally described.
BACKGROUND
Membranes which are selectively permeable to solvent (for example, water) and impermeable to dissolved ions (for example, Na+, Cl) have been used to desalinate aqueous feed solutions. In one such desalination process—generally referred to as forward osmosis—water is transported from a feed solution through the semi-permeable membrane using a solution on the permeate side of the membrane that has an osmotic pressure that is higher than the osmotic pressure of the feed solution. The driving force for separation in a forward osmosis process is the osmotic pressure gradient through the semi-permeable membrane; because the draw solution on one side of the membrane has a higher osmotic pressure than the feed solution on the other side of the membrane, water is drawn through the semi-permeable membrane from the feed solution to the draw solution to equalize the osmotic pressures of the feed and draw solutions.
Another type of membrane-based desalination is reverse osmosis desalination. In contrast to forward osmosis, reverse osmosis processes use an applied hydraulic pressure as the driving force for separation. The applied hydraulic pressure serves to counteract the osmotic pressure gradient that would otherwise favor water flux from low osmotic pressure to high osmotic pressure.
Membrane-based desalination systems have, to date, been limited by, for example, low efficiencies and have generally been limited to treating waters of relatively low salinities. Improved systems and methods for performing membrane-based desalination are desirable.
SUMMARY
Systems and methods for osmotic desalination are disclosed. Certain embodiments are related to the use of a combination of forward osmosis and reverse osmosis to produce a stream comprising a relatively high water purity relative to the water purity of an aqueous feed stream. The subject matter of the present invention involves, in some cases, interrelated products, alternative solutions to a particular problem, and/or a plurality of different uses of one or more systems and/or articles.
Certain embodiments are related to methods, such as methods of performing osmosis. According to some embodiments, the method comprises transporting an aqueous feed stream containing a suspended and/or emulsified immiscible phase and solubilized ions at a concentration of at least about 60,000 ppm across a first side of a first osmotic membrane; and transporting a first draw inlet stream across a second side of the first osmotic membrane, the first draw inlet stream having a higher osmotic pressure than an osmotic pressure of the aqueous feed stream such that water is transported from the aqueous feed stream through the first osmotic membrane to the first draw inlet stream to produce a first draw product stream having a lower osmotic pressure than the first draw inlet stream and a concentrated aqueous stream having a higher concentration of solubilized ions than the aqueous feed stream. Some such embodiments comprise directing the transport of the aqueous feed stream across the first osmotic membrane and/or the first draw inlet stream across the first osmotic membrane such that the following two ratios are within about 20% of each other: a ratio of a mass flow rate of the first draw inlet stream entering the first osmotic membrane to a mass flow rate of the aqueous feed stream entering the first osmotic membrane, and a ratio of the difference between the osmotic pressure of the aqueous feed stream entering the first osmotic membrane and the inlet pressure difference across the first osmotic membrane to the sum of the osmotic pressure of the first draw inlet stream entering the first osmotic membrane and the inlet pressure difference across the first osmotic membrane. Some such embodiments comprise transporting at least a portion of the first draw product stream from the second side of the first osmotic membrane across a first side of a second osmotic membrane; transporting a second draw inlet stream across a second side of the second osmotic membrane; and applying a hydraulic pressure to the first side of the second osmotic membrane such that water is transported from the first draw product stream through the second osmotic membrane to the second draw inlet stream to produce a second draw product stream having a lower osmotic pressure than the second draw inlet stream and a second concentrated aqueous stream having a higher osmotic pressure than the first draw product stream. Some such embodiments comprise directing the transport of the first draw product stream across the second osmotic membrane and/or the second draw inlet stream across the second osmotic membrane such that the following two ratios are within about 20% of each other: a ratio of a mass flow rate of the second draw inlet stream entering the second osmotic membrane to a mass flow rate of the first draw product stream entering the second osmotic membrane, and a ratio of the difference between the osmotic pressure of the first draw product stream entering the second osmotic membrane and the inlet pressure difference across the second osmotic membrane to the sum of the osmotic pressure of the second draw inlet stream entering the second osmotic membrane and the inlet pressure difference across the second osmotic membrane.
Certain embodiments comprise transporting an aqueous feed stream containing a suspended and/or emulsified immiscible phase and solubilized ions at a concentration of at least about 60,000 ppm across a first side of a first osmotic membrane; and transporting a first draw inlet stream across a second side of the first osmotic membrane, the first draw inlet stream having a higher osmotic pressure than an osmotic pressure of the aqueous feed stream such that water is transported from the aqueous feed stream through the first osmotic membrane to the first draw inlet stream to produce a first draw product stream having a lower osmotic pressure than the first draw inlet stream and a concentrated aqueous stream having a higher concentration of solubilized ions than the aqueous feed stream. Some such embodiments comprise directing the transport of the aqueous feed stream across the first osmotic membrane and/or the first draw inlet stream across the first osmotic membrane such that the transmembrane net driving force at the entrance of the aqueous feed stream to the first osmotic membrane and the transmembrane net driving force at the entrance of the first draw inlet stream to the first osmotic membrane are within about 10% of each other. Some such embodiments comprise transporting at least a portion of the first draw product stream from the second side of the first osmotic membrane across a first side of a second osmotic membrane; transporting a second draw inlet stream across a second side of the second osmotic membrane. Some such embodiments comprise applying a hydraulic pressure to the first side of the second osmotic membrane such that water is transported from the first draw product stream through the second osmotic membrane to the second draw inlet stream to produce a second draw product stream having a lower osmotic pressure than the second draw inlet stream and a second concentrated aqueous stream having a higher osmotic pressure than the first draw product stream; and directing the transport of the first draw product stream across the second osmotic membrane and/or the second draw inlet stream across the second osmotic membrane such that the transmembrane net driving force at the entrance of the first draw product stream to the second osmotic membrane and the transmembrane net driving force at the entrance of the second draw inlet stream across the second osmotic membrane are within about 10% of the each other.
According to certain embodiments, the method comprises transporting an aqueous feed stream containing a suspended and/or emulsified immiscible phase and solubilized ions at a concentration of at least about 60,000 ppm across a first side of a first osmotic membrane; transporting a first draw inlet stream across a second side of the first osmotic membrane, the first draw inlet stream having a higher osmotic pressure than an osmotic pressure of the aqueous feed stream such that water is transported from the aqueous feed stream through the first osmotic membrane to the first draw inlet stream to produce a first draw product stream having a lower osmotic pressure than the first draw inlet stream and a concentrated aqueous stream having a higher concentration of solubilized ions than the aqueous feed stream; and directing the transport of the aqueous feed stream across the first osmotic membrane and/or the first draw inlet stream across the first osmotic membrane such that the transmembrane net driving force at the entrance of the aqueous feed stream to the first osmotic membrane and the transmembrane net driving force at the entrance of the first draw inlet stream to the first osmotic membrane are at least about 10% different from each other. Some such embodiments comprise measuring at least one of a temperature, a pressure, a solubilized species concentration, and a flow rate of the aqueous feed stream and/or the first draw inlet stream; and changing at least one of the flow rate of the aqueous feed stream and the flow rate of the first draw inlet stream such that the transmembrane net driving force at the entrance of the aqueous feed stream to the first osmotic membrane and the transmembrane net driving force at the entrance of the first draw inlet stream to the first osmotic membrane are within about 10% of each other. Some such embodiments comprise transporting at least a portion of the first draw product stream from the second side of the first osmotic membrane across a first side of a second osmotic membrane; transporting a second draw inlet stream across a second side of the second osmotic membrane; applying a hydraulic pressure to the first side of the second osmotic membrane such that water is transported from the first draw product stream through the second osmotic membrane to the second draw inlet stream to produce a second draw product stream having a lower osmotic pressure than the second draw inlet stream and a second concentrated aqueous stream having a higher osmotic pressure than the first draw product stream; and directing the transport of the first draw product stream across the second osmotic membrane and/or the second draw inlet stream across the second osmotic membrane such that the transmembrane net driving force at the entrance of the first draw product stream to the second osmotic membrane and the transmembrane net driving force at the entrance of the second draw inlet stream to the second osmotic membrane are at least about 10% different from each other. Some such embodiments comprise measuring at least one of a temperature, a pressure, a solubilized species concentration, and a flow rate of the first draw product stream and/or the second draw inlet stream; and changing at least one of the flow rate of the first draw product stream and the flow rate of the second draw inlet stream such that the transmembrane net driving force at the entrance of the first draw product stream to the second osmotic membrane and the transmembrane net driving force at the entrance of the second draw inlet stream to the second osmotic membrane are within about 10% of each other.
According to certain embodiments, the method comprises transporting an aqueous feed stream containing a suspended and/or emulsified immiscible phase and solubilized ions at a concentration of at least about 60,000 ppm across a first side of a first osmotic membrane; transporting a first draw inlet stream across a second side of the first osmotic membrane, the first draw inlet stream having a higher osmotic pressure than an osmotic pressure of the aqueous feed stream such that water is transported from the aqueous feed stream through the first osmotic membrane to the first draw inlet stream to produce a first draw product stream having a lower osmotic pressure than the first draw inlet stream and a concentrated aqueous stream having a higher concentration of solubilized ions than the aqueous feed stream; transporting at least a portion of the first draw product stream from the second side of the first osmotic membrane across a first side of a second osmotic membrane; transporting a second draw inlet stream across a second side of the second osmotic membrane; and applying a hydraulic pressure to the first side of the second osmotic membrane such that water is transported from the first draw product stream through the second osmotic membrane to the second draw inlet stream to produce a second draw product stream having a lower osmotic pressure than the second draw inlet stream and a second concentrated aqueous stream having a higher osmotic pressure than the first draw product stream. In some such embodiments, the first osmotic membrane is operated such that:
m D 1 , i m F 1 , i = C 1 π F 1 , i - ( P F 1 - P D 1 ) π D 1 , i + ( P F 1 - P D 1 )
wherein PF1 is a hydraulic pressure at an inlet of the aqueous feed stream to the first osmotic membrane; mF1,i is a mass flow rate of the aqueous feed stream at the inlet of the aqueous feed stream to the first osmotic membrane; πF1,i is an osmotic pressure of the aqueous feed stream at the inlet of the aqueous feed stream to the first osmotic membrane; PD1 is a hydraulic pressure at an inlet of the first draw inlet stream to the first osmotic membrane; mD1,i is a mass flow rate of the first draw inlet stream at the inlet of the first draw inlet stream to the first osmotic membrane; πD1,i is an osmotic pressure of the first draw inlet stream at the inlet of the first draw inlet stream to the first osmotic membrane; and C1 is from about 0.8 to about 1.2; and the second osmotic membrane is operated such that:
m D 2 , i m F 2 , i = C 2 π F 2 , i - ( P F 2 - P D 2 ) π D 2 , i + ( P F 2 - P D 2 )
wherein PF2 is a hydraulic pressure at an inlet of the first draw product stream to the second osmotic membrane; mF2,i is a mass flow rate of the first draw product stream at the inlet of the first draw product stream to the second osmotic membrane; πF2,i is an osmotic pressure of the first draw product stream at the inlet of the first draw product stream to the second osmotic membrane; PD2 is a hydraulic pressure at an inlet of the second draw inlet stream to the second osmotic membrane; mD2,i is a mass flow rate of the second draw inlet stream at the inlet of the second draw inlet stream to the second osmotic membrane; πD2,i is an osmotic pressure of the second draw inlet stream at the inlet of the second draw inlet stream to the second osmotic membrane; and C2 is from about 0.8 to about 1.2.
In some embodiments, the method comprises transporting an aqueous feed stream containing solubilized ions across a first side of a first osmotic membrane; transporting a first draw inlet stream across a second side of the first osmotic membrane, the first draw inlet stream having a higher osmotic pressure than an osmotic pressure of the aqueous feed stream such that water is transported from the aqueous feed stream through the first osmotic membrane to the first draw inlet stream to produce a first draw product stream having a lower osmotic pressure than the first draw inlet stream and a concentrated aqueous stream having a higher concentration of solubilized ions than the aqueous feed stream; transporting at least a portion of the first draw product stream from the second side of the first osmotic membrane across a first side of a second osmotic membrane; transporting a second draw inlet stream across a second side of the second osmotic membrane; and applying a hydraulic pressure to the first side of the second osmotic membrane such that water is transported from the first draw product stream through the second osmotic membrane to the second draw inlet stream to produce a second draw product stream having a lower osmotic pressure than the second draw inlet stream and a second concentrated aqueous stream having a higher osmotic pressure than the first draw product stream.
The method comprises, according to certain embodiments, transporting an aqueous feed stream across a first side of an osmotic membrane; and transporting a draw inlet stream across a second side of the osmotic membrane such that water is transported from the aqueous feed stream through the osmotic membrane to the draw inlet stream to produce a draw product stream having a lower osmotic pressure than the draw inlet stream and a concentrated aqueous stream having a higher osmotic pressure than the aqueous feed stream; wherein the osmotic membrane is operated such that:
m D , i m F , i = C 1 π F , i - ( P F - P D ) π D , i + ( P F - P D )
wherein PF is a hydraulic pressure at an inlet of the aqueous feed stream to the osmotic membrane; mF,i is a mass flow rate of the aqueous feed stream at the inlet of the aqueous feed stream to the osmotic membrane; πF1,i is an osmotic pressure of the aqueous feed stream at the inlet of the aqueous feed stream to the osmotic membrane; PD is a hydraulic pressure at an inlet of the draw inlet stream to the osmotic membrane; mD,i is a mass flow rate of the draw inlet stream at the inlet of the draw inlet stream to the osmotic membrane; πD,i is an osmotic pressure of the draw inlet stream at the inlet of the draw inlet stream to the osmotic membrane; and C is from about 0.8 to about 1.2.
According to certain embodiments, the method comprises transporting an aqueous feed stream across a first side of an osmotic membrane; transporting a draw inlet stream across a second side of the osmotic membrane such that water is transported from the aqueous feed stream through the osmotic membrane to the draw inlet stream to produce a draw product stream having a lower osmotic pressure than the draw inlet stream and a concentrated aqueous stream having a higher osmotic pressure than the aqueous feed stream; and directing the transport of the aqueous feed stream across the osmotic membrane and/or the draw inlet stream across the osmotic membrane such that the following two ratios are within about 20% of each other: a ratio of a mass flow rate of the draw inlet stream entering the osmotic membrane to a mass flow rate of the aqueous feed stream entering the osmotic membrane, and a ratio of the difference between the osmotic pressure of the aqueous feed stream entering the osmotic membrane and the inlet pressure difference across the osmotic membrane to the sum of the osmotic pressure of the draw inlet stream entering the osmotic membrane and the inlet pressure difference across the osmotic membrane.
The method comprises, according to some embodiments, transporting an aqueous feed stream across a first side of an osmotic membrane; transporting a draw inlet stream across a second side of the osmotic membrane such that water is transported from the aqueous feed stream through the osmotic membrane to the draw inlet stream to produce a draw product stream having a lower osmotic pressure than the draw inlet stream and a concentrated aqueous stream having a higher osmotic pressure than the aqueous feed stream; and directing the transport of the aqueous feed stream across the osmotic membrane and/or the draw inlet stream across the osmotic membrane such that the transmembrane net driving force at the entrance of the aqueous feed stream to the osmotic membrane and the transmembrane net driving force at the entrance of the draw inlet stream to the osmotic membrane are within about 10% of each other.
The method comprises, according to certain embodiments, transporting an aqueous feed stream across a first side of an osmotic membrane; transporting a draw inlet stream across a second side of the osmotic membrane such that water is transported from the aqueous feed stream through the osmotic membrane to the draw inlet stream to produce a draw product stream having a lower osmotic pressure than the draw inlet stream and a concentrated aqueous stream having a higher osmotic pressure than the aqueous feed stream; directing the transport of the aqueous feed stream across the osmotic membrane and/or the draw inlet stream across the osmotic membrane such that the transmembrane net driving force at the entrance of the aqueous feed stream to the osmotic membrane and the transmembrane net driving force at the entrance of the draw inlet stream to the osmotic membrane are at least about 10% different from each other; measuring at least one of a temperature, a pressure, a solubilized species concentration, and a flow rate of the aqueous feed stream and/or the draw inlet stream; and changing at least one of the flow rate of the aqueous feed stream and the flow rate of the draw inlet stream such that the transmembrane net driving force at the entrance of the aqueous feed stream to the osmotic membrane and the transmembrane net driving force at the entrance of the draw inlet stream to the osmotic membrane are within about 10% of each other.
Other advantages and novel features of the present invention will become apparent from the following detailed description of various non-limiting embodiments of the invention when considered in conjunction with the accompanying figures. In cases where the present specification and a document incorporated by reference include conflicting and/or inconsistent disclosure, the present specification shall control.
BRIEF DESCRIPTION OF THE DRAWINGS
Non-limiting embodiments of the present invention will be described by way of example with reference to the accompanying figures, which are schematic and are not intended to be drawn to scale. In the figures, each identical or nearly identical component illustrated is typically represented by a single numeral. For purposes of clarity, not every component is labeled in every figure, nor is every component of each embodiment of the invention shown where illustration is not necessary to allow those of ordinary skill in the art to understand the invention. In the figures:
FIG. 1A is a schematic illustration of an osmotic membrane separator, according to certain embodiments;
FIG. 1B is a cross-sectional illustration of the osmotic membrane separator shown in FIG. 1A;
FIG. 1C is a front, top, right side perspective view of an osmotic membrane, according to some embodiments;
FIG. 1D is a front, bottom, right side perspective view of the exemplary osmotic membrane illustrated in FIG. 1C;
FIG. 2A is a schematic illustration of an exemplary osmotic desalination system, according to certain embodiments;
FIG. 2B is, according to some embodiments, a schematic illustration of an osmotic desalination system;
FIG. 3A is a schematic illustration of an exemplary osmotic desalination system comprising a forward osmosis separator coupled with a series of reverse osmosis separators, according to certain embodiments;
FIG. 3B is, according to some embodiments, a schematic illustration of an exemplary osmotic desalination system comprising a forward osmosis separator coupled with a series of reverse osmosis separator and including energy recovery apparatuses;
FIG. 4A is a schematic diagram illustrating the operation of an osmotic separator, according to one set of embodiments; and
FIG. 4B is an exemplary plot of osmotic pressure as a function of position across an osmotic membrane, according to one embodiment.
DETAILED DESCRIPTION
Disclosed herein are osmotic desalination methods and associated systems. According to certain embodiments, multiple osmotic membrane separators may be used to perform a series of osmosis steps, such that an output stream having a relatively high water purity—compared to a water purity of an aqueous feed stream—is produced. In some embodiments, multiple draw streams can be used to produce aqueous product streams having sequentially higher purities of water.
Certain embodiments are related to osmotic desalination systems and methods in which forward osmosis is used to produce a first product stream having a relatively high water purity relative to an aqueous feed stream, and reverse osmosis is used to perform a second step (and/or additional steps) on the first product stream. The use of forward osmosis as an initial step—which is generally not prone to fouling—can allow one to shield downstream reverse osmosis processes from fouling-causing contaminants. According to certain embodiments, the use of reverse osmosis in subsequent, downstream steps can also allow one to take advantage of the low energy consumption of reverse osmosis relative to, for example, thermal desalination processes such as thermal evaporation/distillation. Employing combinations of forward and reverse osmosis steps in this way can, according to certain embodiments, produce a low-energy, low-fouling desalination system that produces a product stream with a high water purity (and low salinity) relative to an aqueous feed stream.
In some embodiments, multiple reverse osmosis steps can be used in series as part of a system to perform net desalination (i.e., to produce a product stream having a relatively high purity of water compared to the purity of water in an inlet aqueous stream). In some such embodiments, rather than achieving a relatively high water purity through the use of a single membrane, multiple steps can be performed, each achieving a relatively small increase in purity to produce a final product that contains a higher purity of water than the aqueous feed stream. Such arrangements may be useful, for example, when desalinating aqueous feed streams with very high osmotic pressures (e.g., osmotic pressures of 60 bar, or greater). As an exemplary, non-limiting illustration, if one desires to desalinate an aqueous feed stream with an osmotic pressure of 60 bar using a single osmotic membrane, one would need to use a mechanically robust osmotic membrane capable of withstanding very high hydraulic pressures (e.g., above 60 bar). Such membranes are typically difficult and expensive to manufacture. Certain embodiments employ the recognition that the use of multiple reverse osmosis membranes, each operated using relatively low hydraulic pressure gradients, can be used to perform a stepwise process in which each reverse osmosis step gradually increases the purity of water until the desired final level of water purity is achieved.
Certain embodiments relate to systems and methods in which strategies are employed to reduce energy consumption in osmotic desalination systems. According to certain embodiments, the osmotic desalination membrane(s) can be operated such that the transmembrane net driving force (i.e., the net driving force through the thickness of the membrane) is relatively uniform across the facial area of the membrane(s). Such uniformity may, according to certain embodiments, reduce or eliminate unnecessary over-pressurization along the osmotic membrane, which can in turn reduce or eliminate wasted energy during operation of the system.
As described in more detail below, certain of the systems and methods described herein can be used to treat a wide variety of aqueous feed streams, including but not limited to streams derived from seawater, ground water, brackish water, and/or the effluent of a chemical process. In certain embodiments, the aqueous feed stream contains a relatively large amount of solubilized ions, for example, at a concentration of at least about 60,000 ppm. In certain embodiments, the aqueous feed contains, in addition to ions solubilized in water, a suspended and/or emulsified phase that is immiscible in water (e.g., oil and/or grease).
Certain embodiments are related to the use of osmotic membrane-based systems to perform desalination. FIG. 1A is an exemplary schematic diagram illustrating the use of an osmotic membrane separator to desalinate an aqueous feed stream. FIG. 1B is a cross-sectional illustration of the schematic shown in FIG. 1A.
In FIGS. 1A-1B, osmotic membrane 102 can be used to transport water from first side 104 to second side 106. In some cases, this may result in at least partial separation of water within aqueous feed stream 108 from solubilized ions (or other solubilized species) within aqueous feed stream 108. Aqueous feed stream 108 can be transported across first side 104 of osmotic membrane 102, for example, in the direction of arrow 103 in FIG. 1B. Draw inlet stream 110 can, in some embodiments, be transported across second side 106 of osmotic membrane 102, for example, in the direction of arrow 105 in FIG. 1B.
Transport of water through the osmotic membrane can be achieved via a transmembrane net driving force (i.e., a net driving force through the thickness of the membrane), according to certain embodiments. Generally, the transmembrane net driving force (Δχ) is expressed as:
Δχ =ΔP−ΔΠ=(P 1 −P 2)−(Π1−Π2)  [1]
wherein P1 is the hydraulic pressure on the first (retentate) side of the osmotic membrane, P2 is the hydraulic pressure on the second (permeate) side of the osmotic membrane, Π1 is the osmotic pressure of the stream on the first (retentate) side of the osmotic membrane, and Π2 is the osmotic pressure of the stream on the second (permeate) side of the osmotic membrane. (P1−P2) can be referred to as the transmembrane hydraulic pressure gradient, and (Π1−Π2) can be referred to as the transmembrane osmotic pressure gradient.
Those of ordinary skill in the art are familiar with the concept of osmotic pressure. The osmotic pressure of a particular liquid is an intrinsic property of the liquid. The osmotic pressure can be determined in a number of ways, with the most efficient method depending upon the type of liquid being analyzed. For certain solutions with relatively low molar concentrations of ions, osmotic pressure can be accurately measured using an osmometer. In other cases, the osmotic pressure can simply be determined by comparison with solutions with known osmotic pressures. For example, to determine the osmotic pressure of an uncharacterized solution, one could apply a known amount of the uncharacterized solution on one side of a non-porous, semi-permeable, osmotic membrane and iteratively apply different solutions with known osmotic pressures on the other side of the osmotic membrane until the differential pressure through the thickness of the membrane is zero.
The osmotic pressure (Π) of a solution containing n solubilized species may be estimated as:
Π=Σj=1 n i j M j RT  [2]
wherein ij is the van't Hoff factor of the jth solubilized species, Mj is the molar concentration of the jth solubilized species in the solution, R is the ideal gas constant, and T is the absolute temperature of the solution. Equation 2 generally provides an accurate estimate of osmotic pressure for liquid with low concentrations of solubilized species (e.g., concentrations at or below between about 4 wt % and about 6 wt %). For many liquid comprising solubilized species, at species concentrations above around 4-6 wt %, the increase in osmotic pressure per increase in salt concentration is greater than linear (e.g., slightly exponential).
Certain of the osmotic membrane separators described herein can be used to perform forward osmosis. Forward osmosis generally occurs when the osmotic pressure on the second (permeate) side of the osmotic membrane is greater than the osmotic pressure on the first (retentate) side of the osmotic membrane such that water is transported from the first side of the osmotic membrane to the second side of the osmotic membrane. In forward osmosis systems, water generally is transported from the first side of the osmotic membrane to the second side of the osmotic membrane as long as the hydraulic pressure difference between the second side of the osmotic membrane and the first side of the osmotic membrane is not sufficiently high to overcome the osmotic pressure difference between the first and second sides of the osmotic membrane. In this way, the permeate flow and the osmotic driving force are aligned in the same direction. In forward osmosis arrangements, the stream on the second side of the osmotic membrane can initiate the transport of water from the stream of the first side of the osmotic membrane through the osmotic membrane from the first side to the second side, resulting in the production of a stream having a higher osmotic pressure (e.g., more concentrated in solubilized species (e.g., dissolved ions and/or disassociated molecules)) relative to the aqueous feed stream. For example, referring to FIGS. 1A-1B, osmotic membrane 102 can be used to perform forward osmosis, for example, when the osmotic pressure on second side 106 is higher than the osmotic pressure on first side 104, and the hydraulic pressure gradient from second side 106 to first side 104 (P106−P104) is not large enough to overcome the difference in the osmotic pressures on first side 104 and second side 106. In such cases, water can be transported from first side 104 of osmotic membrane 102 to second side 106 of osmotic membrane 102. This can result, according to certain embodiments, in the production of stream 114, which can have a higher osmotic pressure than the osmotic pressure of stream 108. In certain embodiments in which stream 108 contains solubilized species (e.g., ions), the forward osmosis process can result in the production of concentrated aqueous stream 114, which can contain solubilized species (e.g., ions) at a molar concentration greater than the molar concentration of solubilized species (e.g., ions) in stream 108. In addition, the forward osmosis process can result, according to some embodiments, in the production of draw product stream 112, which can have a lower osmotic pressure than the osmotic pressure of stream 110. For example, when solubilized species are used in the draw stream, the draw product stream 112 can contain the solubilized species (e.g., ions) at a lower molar concentration than the molar concentration of solubilized species (e.g., ions) within stream 110.
In some cases, pressure may be applied to enhance the forward osmosis process. For example, in some instances in which the stream on the first side of the osmotic membrane has a lower osmotic pressure than the stream on the second side of the osmotic membrane, pressure may be applied to the first side of the osmotic membrane such that the hydraulic pressure of the stream on the first side of the osmotic membrane is higher than the hydraulic pressure of the stream on the second side of the osmotic membrane. The applied pressure can increase the rate at which water is transported from the first side of the osmotic membrane to the second side of the osmotic membrane. Such arrangements are sometimes referred to herein as pressure-assisted forward osmosis. Of course, the use of an applied pressure to enhance forward osmosis is not generally required, and in some embodiments, forward osmosis is performed in the substantial absence of an applied pressure (e.g., such that the hydraulic pressure gradient through the osmotic membrane is less than or equal to about 0.1 bar).
Osmotic membranes can be used, according to certain embodiments, to perform reverse osmosis. Reverse osmosis generally occurs when the osmotic pressure on the first (retentate) side of the osmotic membrane is greater than the osmotic pressure on the second (permeate) side of the osmotic membrane, and a pressure is applied to the first side of the osmotic membrane such that the hydraulic pressure on the first side of the osmotic membrane is sufficiently greater than the hydraulic pressure on the second side of the osmotic membrane to cause water to be transported from the first side of the osmotic membrane to the second side of the osmotic membrane. Generally, such situations result when the transmembrane hydraulic pressure gradient (P1−P2) is greater than the transmembrane osmotic pressure gradient (Π1−Π2) such that water is transported from the first side of the osmotic membrane to the second side of the osmotic membrane (rather than having water transported from the second side of the osmotic membrane to the first side of the osmotic membrane, which would be energetically favored in the absence of the pressure applied to the first side of the osmotic membrane). Referring to FIGS. 1A-1B, osmotic membrane 102 can be used to perform reverse osmosis, for example, when the osmotic pressure on first side 104 is higher than the osmotic pressure on second side 106, a pressure is applied to first side such that the hydraulic pressure on first side 104 is higher than the hydraulic pressure on second side 106, and the difference between the hydraulic pressure on first side 104 and the hydraulic pressure on second side 106 is greater than the difference between the osmotic pressure on side 104 and the osmotic pressure on side 106. In such cases, water can be transported from first side 104 of osmotic membrane 102 to second side 106 of osmotic membrane 102. This can result, according to certain embodiments, in the production of stream 114, which can have a higher osmotic pressure than stream 108. For example, when solubilized species (e.g., ions) are employed in stream 108, the reverse osmosis process can result, according to certain embodiments, in the production of concentrated aqueous stream 114, which can contain solubilized species (e.g., ions) at a molar concentration greater than the molar concentration of solubilized species (e.g., ions) in stream 108. In addition, this can result, according to some embodiments, in the production of draw product stream 112, which can have a lower osmotic pressure than the osmotic pressure of stream 110. For example, when solubilized species (e.g., ions) are employed in draw inlet stream 110, according to some embodiments, the reverse osmosis process can result in the production of draw product stream 112, which can contain solubilized species (e.g., ions) at a lower molar concentration than the molar concentration of solubilized species (e.g., ions) within stream 110.
Certain embodiments are related to desalination systems and methods comprising an initial forward osmosis desalination step and one or more downstream reverse osmosis steps. FIG. 2A is a schematic illustration of an exemplary desalination system 200, according to certain embodiments. In FIG. 2A, desalination system 200 comprises first osmotic membrane 202, which has first side 204 and second side 206. Desalination system 200 also comprises second osmotic membrane 216, which has first side 218 and second side 220. According to certain embodiments, the first osmotic membrane can be used to perform a first osmosis step, and the second osmotic membrane can be used to perform a second osmosis step. For example, in some embodiments, first osmotic membrane 202 can be used to perform a first osmosis step (e.g., a forward osmosis step), and second osmotic membrane 216 can be used to perform a second osmosis step (e.g., a reverse osmosis step).
Certain embodiments comprise transporting an aqueous feed stream containing solubilized ions across a first side of a first osmotic membrane. For example, referring to FIG. 2A, in some embodiments, aqueous feed stream 208 containing solubilized ions can be transported across first side 204 of first osmotic membrane 202. Some embodiments comprise transporting a first draw inlet stream across a second side of the first osmotic membrane. For example, referring to FIG. 2A, in certain embodiments, first draw inlet stream 210 can be transported across second side 206 of first osmotic membrane 202.
In some embodiments, the first draw inlet stream has a higher osmotic pressure than the osmotic pressure of the aqueous feed stream (e.g., due to a higher molar concentration of total solubilized species within the first draw inlet stream than in the aqueous feed stream). In some such embodiments, the osmotic pressure of the first draw inlet stream is higher than the osmotic pressure of the aqueous feed stream such that water is transported from the aqueous feed stream through the first osmotic membrane to the first draw inlet stream. In some such embodiments, this process can produce a first draw product stream having a lower osmotic pressure than the first draw inlet stream (e.g., due to a lower molar concentration of solubilized species in the first draw product stream than in the first draw inlet stream). In some cases, the process can also produce a concentrated aqueous stream having a higher molar concentration of solubilized ions than the aqueous feed stream. For example, in FIG. 2A, first draw inlet stream 210 can, in some embodiments, have an osmotic pressure that is sufficiently high such that water is transported from aqueous feed stream 208 through first osmotic membrane 202 to first draw inlet stream 210. Transport of water through osmotic membrane 202 can result in the production of first draw product stream 212 having a lower osmotic pressure than first draw inlet stream 210 (e.g., due to a lower molar concentration of solubilized species (e.g., ions) within draw product stream 212 than in draw inlet stream 210). Transport of water through osmotic membrane 202 can also result in the production of concentrated aqueous stream 214 having a higher molar concentration of solubilized ions than aqueous feed stream 208.
In certain embodiments, the concentrated aqueous stream (e.g., 214 in FIGS. 2A-2B) can have an osmotic pressure that is at least about 1.01 times, at least about 1.1 times, at least about 1.5 times, at least about 2 times, at least about 5 times, at least about 10 times, or at least about 50 times (and/or, in some embodiments, up to about 100 times, up to about 500 times, up to about 1000 times, up to about 5000 times, or more) the osmotic pressure of the aqueous feed stream (e.g., stream 208 in FIGS. 2A-2B).
In some embodiments, the concentrated aqueous stream (e.g., 214 in FIGS. 2A-2B) can have a weight percentage of solubilized species (e.g., ions) that is at least about 1.01 times, at least about 1.1 times, at least about 1.5 times, at least about 2 times, at least about 5 times, at least about 10 times, or at least about 50 times (and/or, in some embodiments, up to about 100 times, up to about 500 times, up to about 1000 times, up to about 5000 times, or more) the weight percentage of solubilized species (e.g., ions) in the aqueous feed stream (e.g., stream 208 in FIGS. 2A-2B). For example, referring to FIGS. 2A-2B, in some embodiments, first aqueous feed stream 208 can have a solubilized ion concentration of 10 wt % and first concentrated aqueous stream 214 can have a solubilized ion concentration of 20 wt %, which is 2 times the weight percentage of solubilized ions in the first aqueous feed stream.
In certain embodiments, the first draw inlet stream (e.g., stream 210 in FIGS. 2A-2B) can have an osmotic pressure that is at least about 1.01 times, at least about 1.1 times, at least about 1.5 times, at least about 2 times, at least about 5 times, at least about 10 times, or at least about 50 times (and/or, in some embodiments, up to about 100 times, up to about 500 times, up to about 1000 times, up to about 5000 times, or more) the osmotic pressure of the first draw product stream (e.g., stream 212 in FIGS. 2A-2B).
In certain embodiments, the first draw inlet stream (e.g., stream 210 in FIGS. 2A-2B) can have a weight percentage of solubilized species (e.g., ions) that is at least about 1.01 times, at least about 1.1 times, at least about 1.5 times, at least about 2 times, at least about 5 times, at least about 10 times, or at least about 50 times (and/or, in some embodiments, up to about 100 times, up to about 500 times, up to about 1000 times, up to about 5000 times, or more) the weight percentage of solubilized ions in the first draw product stream (e.g., stream 212 in FIGS. 2A-2B). For example, referring to FIGS. 2A-2B, in some embodiments, first draw product stream 212 can have a solubilized ion concentration of 12 wt % and first draw inlet stream 210 can have a solubilized ion concentration of 20 wt %, which is 1.67 times the weight percentage of solubilized ions in the first draw product stream.
In certain embodiments, the first osmotic membrane separator can be operated as a forward osmosis membrane separator. For example, in some embodiments, the osmotic pressure of the stream on the first side of the first osmotic membrane can be lower than the osmotic pressure of the stream on the second side of the first osmotic membrane such that water is transported from the first side of the first osmotic membrane to the second side of the first osmotic membrane, at least in part, due to the transmembrane osmotic pressure difference. In some embodiments, the forward osmosis process can be carried out in the substantial absence of an applied hydraulic pressure on the first side of the osmotic membrane. For example, referring to FIG. 2A, in some embodiments, forward osmosis can be performed using osmotic membrane 202 (e.g., as described above) in the substantial absence of a hydraulic pressure applied to the liquid on first side 204 of osmotic membrane 202. In other cases, the forward osmosis process can be a pressure-assisted forward osmosis process, in which a substantial hydraulic pressure is applied to the first side of the osmotic membrane. For example, referring to FIG. 2A, in some embodiments, forward osmosis can be performed using osmotic membrane 202 (e.g., as described above) while a hydraulic pressure is applied to the liquid on first side 204 of osmotic membrane 202.
Certain embodiments comprise transporting at least a portion of the first draw product stream from the second side of the first osmotic membrane across a first side of a second osmotic membrane. For example, referring to FIG. 2A, in some embodiments, at least a portion of first draw product stream 212 can be transported across first side 218 of the second osmotic membrane 216. Some embodiments comprise transporting a second draw inlet stream across a second side of the second osmotic membrane. For example, in the exemplary embodiment shown in FIG. 2A, second draw inlet stream 222 can be transported across second side 220 of second osmotic membrane 216.
Certain embodiments comprise applying a hydraulic pressure to the first side of the second osmotic membrane such that water is transported from the first draw product stream through the second osmotic membrane to the second draw inlet stream to produce a second draw product stream having a lower osmotic pressure (e.g., due to a lower molar concentration of solubilized species (e.g., ions)) than the second draw inlet stream and a second concentrated aqueous stream having a higher osmotic pressure (e.g., due to a higher molar concentration of solubilized species (e.g., ions)) than the first draw product stream. For example, referring to FIG. 2A, in some embodiments, a hydraulic pressure is applied to first side 218 of second osmotic membrane 216 such that water is transported from first draw product stream 212 through second osmotic membrane 216 to second draw inlet stream 222 to produce second draw product stream 224 having a lower osmotic pressure (e.g., due to a lower molar concentration of solubilized species (e.g., ions)) than second draw inlet stream 222 and second concentrated aqueous stream 226 having a higher osmotic pressure (e.g., due to a higher molar concentration of solubilized species (e.g., ions)) than first draw product stream 212.
In some embodiments, the second concentrated aqueous stream (e.g., 226 in FIGS. 2A-2B) can have an osmotic pressure that is at least about 1.01 times, at least about 1.1 times, at least about 1.5 times, at least about 2 times, at least about 5 times, at least about 10 times, or at least about 50 times (and/or, in some embodiments, up to about 100 times, up to about 500 times, up to about 1000 times, up to about 5000 times, or more) the osmotic pressure of the first draw product stream (e.g., stream 212 in FIGS. 2A-2B).
In some embodiments, the second concentrated aqueous stream (e.g., 226 in FIGS. 2A-2B) can have a weight percentage of solubilized species (e.g., ions) that is at least about 1.01 times, at least about 1.1 times, at least about 1.5 times, at least about 2 times, at least about 5 times, at least about 10 times, or at least about 50 times (and/or, in some embodiments, up to about 100 times, up to about 500 times, up to about 1000 times, up to about 5000 times, or more) the weight percentage of solubilized species (e.g., ions) in the first draw product stream (e.g., stream 212 in FIGS. 2A-2B). For example, referring to FIGS. 2A-2B, in some embodiments, first draw product stream 212 can have a solubilized ion concentration of 12 wt % and second concentrated aqueous stream 226 can have a solubilized ion concentration of 22 wt %, which is 1.83 times the weight percentage of solubilized ions in the first draw product stream.
In certain embodiments, the second draw inlet stream (e.g., stream 222 in FIGS. 2A-2B) can have an osmotic pressure that is at least about 1.01 times, at least about 1.1 times, at least about 1.5 times, at least about 2 times, at least about 5 times, at least about 10 times, or at least about 50 times (and/or, in some embodiments, up to about 100 times, up to about 500 times, up to about 1000 times, up to about 5000 times, or more) the osmotic pressure of the second draw product stream (e.g., stream 224 in FIGS. 2A-2B).
In certain embodiments, the second draw inlet stream (e.g., stream 222 in FIGS. 2A-2B) can have a weight percentage of solubilized species (e.g., ions) that is at least about 1.01 times, at least about 1.1 times, at least about 1.5 times, at least about 2 times, at least about 5 times, at least about 10 times, or at least about 50 times (and/or, in some embodiments, up to about 100 times, up to about 500 times, up to about 1000 times, up to about 5000 times, or more) the weight percentage of solubilized species (e.g., ions) in the second draw product stream (e.g., stream 224 in FIGS. 2A-2B). For example, referring to FIGS. 2A-2B, in some embodiments, second draw product stream 224 can have a solubilized ion concentration of 10 wt % and second draw inlet stream 222 can have a solubilized ion concentration of 20 wt %, which is 2 times the weight percentage of solubilized ions in the second draw product stream.
The second osmotic membrane separator can be operated as a reverse osmosis membrane separator, according to certain embodiments. That is to say, in some embodiments, water can be transported from the first side of the second osmotic membrane to the second side of the second osmotic membrane by applying a hydraulic pressure to the first side of the second osmotic membrane as a driving force, such that local osmotic pressure gradients through the thickness of the membrane that would otherwise favor the transport of water from the second side of the membrane to the first side of the membrane are overcome by the applied hydraulic pressure. In some embodiments, the osmotic pressure of the stream on the first side of the second osmotic membrane can be higher than the osmotic pressure of the stream on the second side of the second osmotic membrane, such that water is transported through the second osmotic membrane due to a hydraulic pressure applied to the first side of the second osmotic membrane.
As noted above, certain embodiments are related to desalination systems and methods in which multiple reverse osmosis steps are performed in series. FIG. 2B is a schematic illustration of an exemplary desalination system 260, according to certain embodiments. In FIG. 2B, desalination system 260 comprises first osmotic membrane 202 (which comprises first side 204 and second side 206) and second osmotic membrane 216 (which comprises first side 218 and second side 220). According to certain embodiments, first osmotic membrane 202 and second osmotic membrane 216 can be operated as described elsewhere herein with respect to membranes 202 and 216 (e.g., as shown in FIG. 2A). System 260 in FIG. 2B further comprises a third osmotic membrane 228, comprising first side 230 and second side 232. System 260 also comprises optional fourth osmotic membrane 240, comprising first side 242 and second side 244. According to certain embodiments, the first osmotic membrane can be used to perform a first osmosis step, the second osmotic membrane can be used to perform a second osmosis step, and the third osmotic membrane can be used to perform a third osmosis step. The fourth osmotic membrane, when present, can be used to perform a fourth osmosis step, according to certain embodiments. As one example, in some embodiments, first osmotic membrane 202 can be used to perform a first osmosis step (e.g., a forward osmosis desalination step), second osmotic membrane 216 can be used to perform a second osmosis step (e.g., a first reverse osmosis desalination step), and third osmotic membrane 228 can be used to perform a third osmosis step (e.g., a second reverse osmosis desalination step). When present, optional fourth osmotic membrane can be used to perform a fourth osmosis step (e.g., a third reverse osmosis step).
According to some embodiments, first osmotic membrane 202 and second osmotic membrane 216 can be operated as described elsewhere. Some embodiments comprise transporting at least a portion of the second draw product stream from the second side of the second osmotic membrane across a first side of a third osmotic membrane. For example, referring to FIG. 2B, in some embodiments, at least a portion of second draw product stream 224 is transported from the second side 220 of the second osmotic membrane 216 across first side 230 of third osmotic membrane 228. Certain embodiments comprise transporting a third draw inlet stream across a second side of the third osmotic membrane. For example, referring to FIG. 2B, in some embodiments, third draw inlet stream 234 is transported across second side 232 of third osmotic membrane 228.
Some embodiments comprise applying a hydraulic pressure to the second draw product stream on the first side of the third osmotic membrane such that water is transported from the second draw product stream through the third osmotic membrane to the third draw inlet stream to produce a third draw product stream having a lower osmotic pressure (e.g., due to a lower molar concentration of solubilized species (e.g., ions)) than the third draw inlet stream and a third concentrated stream having a higher osmotic pressure (e.g., due to a higher molar concentration of solubilized species (e.g., ions)) than the second draw product stream. For example, referring to FIG. 2B, in some embodiments, a hydraulic pressure is applied to second draw product stream 224 on first side 230 of third osmotic membrane 228 such that water is transported from second draw product stream 224 through third osmotic membrane 228 to third draw inlet stream 234 to produce third draw product stream 236 having a lower osmotic pressure (e.g., due to a lower molar concentration of solubilized species (e.g., ions)) than third draw inlet stream 234 and third concentrated aqueous stream 238 having a higher osmotic pressure (e.g., due to a higher molar concentration of solubilized species (e.g., ions)) than second draw product stream 224.
In certain embodiments, the third concentrated aqueous stream (e.g., 238 in FIG. 2B) can have an osmotic pressure that is at least about 1.01 times, at least about 1.1 times, at least about 1.5 times, at least about 2 times, at least about 5 times, at least about 10 times, or at least about 50 times (and/or, in some embodiments, up to about 100 times, up to about 500 times, up to about 1000 times, up to about 5000 times, or more) the osmotic pressure of the second draw product stream (e.g., stream 224 in FIG. 2B).
In some embodiments, the third concentrated aqueous stream (e.g., 238 in FIG. 2B) can have a weight percentage of solubilized species (e.g., ions) that is at least about 1.01 times, at least about 1.1 times, at least about 1.5 times, at least about 2 times, at least about 5 times, at least about 10 times, or at least about 50 times (and/or, in some embodiments, up to about 100 times, up to about 500 times, up to about 1000 times, up to about 5000 times, or more) the weight percentage of solubilized species (e.g., ions) in the second draw product stream (e.g., stream 224 in FIG. 2B). For example, referring to FIG. 2B, in some embodiments, second draw product stream 224 can have a solubilized ion concentration of 10 wt % and third concentrated aqueous stream 238 can have a solubilized ion concentration of 20 wt %, which is 2 times greater than the weight percentage of solubilized ions in the second draw product stream.
In certain embodiments, the third draw inlet stream (e.g., stream 234 in FIG. 2B) can have an osmotic pressure that is at least about 1.01 times, at least about 1.1 times, at least about 1.5 times, at least about 2 times, at least about 5 times, at least about 10 times, or at least about 50 times (and/or, in some embodiments, up to about 100 times, up to about 500 times, up to about 1000 times, up to about 5000 times, or more) the osmotic pressure of the third draw product stream (e.g., stream 236 in FIG. 2B).
In certain embodiments, the third draw inlet stream (e.g., stream 234 in FIG. 2B) can have a weight percentage of solubilized species (e.g., ions) that is at least about 1.01 times, at least about 1.1 times, at least about 1.5 times, at least about 2 times, at least about 5 times, at least about 10 times, or at least about 50 times (and/or, in some embodiments, up to about 100 times, up to about 500 times, up to about 1000 times, up to about 5000 times, or more) the weight percentage of solubilized species (e.g., ions) in the third draw product stream (e.g., stream 236 in FIG. 2B). For example, referring to FIG. 2B, in some embodiments, third draw product stream 236 can have a solubilized ion concentration of 8 wt % and third draw inlet stream 234 can have a solubilized ion concentration of 18 wt %, which is 2.25 times greater than the weight percentage of solubilized ions in the third draw product stream.
The third osmotic membrane separator can be operated as a reverse osmosis membrane separator, according to certain embodiments. That is to say, in some embodiments, water can be transported from the first side of the third osmotic membrane to the second side of the third osmotic membrane by applying a hydraulic pressure to the first side of the third osmotic membrane as a driving force, such that local osmotic pressure gradients through the thickness of the membrane that would otherwise favor the transport of water from the second side of the membrane to the first side of the membrane are overcome by the applied hydraulic pressure. In some embodiments, the osmotic pressure of the stream on the first side of the third osmotic membrane can be higher than the osmotic pressure of the stream on the second side of the third osmotic membrane, such that water is transported through the third osmotic membrane due to a hydraulic pressure applied to the first side of the third osmotic membrane.
In some embodiments, fourth, fifth, sixth, or more osmotic membranes can be used. System 260 in FIG. 2B, according to some embodiments, comprises optional fourth osmotic membrane 240, which comprises first side 242 and second side 244. Some embodiments comprise transporting at least a portion of the third draw product stream from the second side of the third osmotic membrane across a first side of a fourth osmotic membrane. For example, referring to FIG. 2B, in some embodiments, at least a portion of third draw product stream 236 is transported from second side 232 of third osmotic membrane 228 across first side 242 of fourth osmotic membrane 240. Certain embodiments comprise transporting a fourth draw inlet stream across a second side of the fourth osmotic membrane. For example, referring to FIG. 2B, in some embodiments, fourth draw inlet stream 246 is transported across second side 244 of fourth osmotic membrane 240.
Some embodiments comprise applying a hydraulic pressure to the third draw product stream on the first side of the fourth osmotic membrane such that water is transported from the third draw product stream through the fourth osmotic membrane to the fourth draw inlet stream to produce a fourth draw product stream having a lower osmotic pressure (e.g., due to a lower molar concentration of solubilized species (e.g., ions)) than the fourth draw inlet stream and a fourth concentrated aqueous stream having a higher osmotic pressure (e.g., due to a higher molar concentration of solubilized species (e.g., ions)) than the third draw product stream. For example, referring to FIG. 2B, in some embodiments, a hydraulic pressure is applied to third draw product stream 236 on first side 242 of fourth osmotic membrane 240 such that water is transported from third draw product stream 236 through fourth osmotic membrane 240 to fourth draw inlet stream 246 to produce fourth draw product stream 248 having a lower osmotic pressure (e.g., due to a lower molar concentration of solubilized species (e.g., ions)) than fourth draw inlet stream 246 and fourth concentrated aqueous stream 250 having a higher osmotic pressure (e.g., due to a higher molar concentration of solubilized species (e.g., ions) than third draw product stream 236.
In some embodiments, the fourth concentrated aqueous stream (e.g., 250 in FIG. 2B) can have an osmotic pressure that is at least about 1.01 times, at least about 1.1 times, at least about 1.5 times, at least about 2 times, at least about 5 times, at least about 10 times, or at least about 50 times (and/or, in some embodiments, up to about 100 times, up to about 500 times, up to about 1000 times, up to about 5000 times, or more) the osmotic pressure of the third draw product stream (e.g., stream 236 in FIG. 2B).
In some embodiments, the fourth concentrated aqueous stream (e.g., 250 in FIG. 2B) can have a weight percentage of solubilized ions that is at least about 1.01 times, at least about 1.1 times, at least about 1.5 times, at least about 2 times, at least about 5 times, at least about 10 times, or at least about 50 times (and/or, in some embodiments, up to about 100 times, up to about 500 times, up to about 1000 times, up to about 5000 times, or more) the weight percentage of solubilized ions in the third draw product stream (e.g., stream 236 in FIG. 2B).
In certain embodiments, the fourth draw inlet stream (e.g., stream 246 in FIG. 2B) can have an osmotic pressure that is at least about 1.01 times, at least about 1.1 times, at least about 1.5 times, at least about 2 times, at least about 5 times, at least about 10 times, or at least about 50 times (and/or, in some embodiments, up to about 100 times, up to about 500 times, up to about 1000 times, up to about 5000 times, or more) the osmotic pressure of the fourth draw product stream (e.g., stream 248 in FIG. 2B).
In certain embodiments, the fourth draw inlet stream (e.g., stream 246 in FIG. 2B) can have a weight percentage of solubilized ions that is at least about 1.01 times, at least about 1.1 times, at least about 1.5 times, at least about 2 times, at least about 5 times, at least about 10 times, or at least about 50 times (and/or, in some embodiments, up to about 100 times, up to about 500 times, up to about 1000 times, up to about 5000 times, or more) the weight percentage of solubilized ions in the fourth draw product stream (e.g., stream 248 in FIG. 2B).
The fourth osmotic membrane separator can be operated as a reverse osmosis membrane, according to certain embodiments. That is to say, in some embodiments, water can be transported from the first side of the fourth osmotic membrane to the second side of the fourth osmotic membrane by applying a hydraulic pressure to the first side of the fourth osmotic membrane as a driving force, such that local osmotic pressure gradients through the thickness of the membrane that would otherwise favor the transport of water from the second side of the membrane to the first side of the membrane are overcome by the applied hydraulic pressure. In some embodiments, the osmotic pressure of the stream on the first side of the fourth osmotic membrane can be higher than the osmotic pressure of the stream on the second side of the fourth osmotic membrane, such that water is transported through the fourth osmotic membrane due to a hydraulic pressure applied to the first side of the fourth osmotic membrane.
Certain of the systems and methods described herein can be employed such that, during operation, the transmembrane net driving force (i.e., the net driving force through the thickness of the osmotic membrane) is spatially uniform across the facial area of the osmotic membrane. As described above, the transmembrane net driving force is defined as the difference between the transmembrane hydraulic pressure gradient and the transmembrane osmotic pressure gradient, as shown in Equation 1. In some embodiments, over at least about 90%, at least about 95%, at least about 98%, or at least about 99% of the facial area of the osmotic membrane (e.g., the first osmotic membrane, the second osmotic membrane, the third osmotic membrane (if present), and/or the fourth osmotic membrane (if present)), the transmembrane net driving force is uniform to within about 10%, within about 5%, within about 3%, within about 2%, or within about 1%.
The transmembrane net driving force at any given location across the facial area of the osmotic membrane is determined by measuring the properties of the streams on opposite sides of the osmotic membrane at that location. Specifically, one would measure the hydraulic pressure on opposite sides of the osmotic membrane at that location and the osmotic pressure on opposite sides of the osmotic membrane at that location. The transmembrane net driving force could then be calculated using Equation 1 above. As a specific example, referring to FIG. 1B, the transmembrane net driving force at point 150 of osmotic membrane 102 can be determined by measuring the hydraulic pressure of the stream on side 104 at point 150 (P150); the osmotic pressure of the stream on side 104 at point 150150); the hydraulic pressure of the stream on side 106 at point 152 (P152), which is opposite point 150; and the osmotic pressure of the stream on side 106 at point 152152). The transmembrane net driving force at point 150χ150) would then be calculated as:
Δχ150 =ΔP−ΔΠ=(P 150 −P 152)−(Π150−Π152)  [3]
To determine the percentage of facial area over which the transmembrane net driving force is uniform, one would measure the transmembrane net driving force at points across the two-dimensional facial area of the osmotic membrane (e.g., at points across facial area 163 shown in FIG. 1C, defined by dimensions 160 and 161), and determine the spatially averaged transmembrane net driving force. The transmembrane net driving force at a particular location would be said to be uniform to within X % if the transmembrane net driving force at that location is within X % of the transmembrane net driving force spatially averaged over the facial area of the osmotic membrane (also referred to herein as the spatially-averaged transmembrane net driving force).
To determine the spatially-averaged transmembrane net driving force across the facial area of an osmotic membrane, one would calculate the transmembrane net driving force (using Equation 1) at each point across the facial area of the osmotic membrane (to produce a two-dimensional distribution of transmembrane net driving forces) and spatially average the distribution of the transmembrane net driving force. To illustrate an exemplary calculation, reference is made to FIGS. 1C-ID. FIG. 1C is a front, top, right side perspective view of an osmotic membrane 102, and FIG. 1D is a front, bottom, right side perspective view of the osmotic membrane 102 of FIG. 1C. In FIGS. 1C-ID, osmotic membrane 102 includes first side 104 and second side 106. Osmotic membrane 102 also comprises a facial area 163 defined by dimensions 160 and 161. To determine the spatially-averaged transmembrane net driving force across facial area 163 of osmotic membrane 102 in FIGS. 1C-1D, one would calculate the two-dimensional distribution of the transmembrane net driving force (using Equation 1) at each point across facial area 163 of osmotic membrane 102. For example, in FIGS. 1C-ID, Equation 1 would be used to determine the transmembrane net driving force between points 150A and 152A, between points 150B and 152B, between points 150C and 152C, between points 150D and 152D, between points 150E and 152E, and at a statistically representative number of point pairs across facial area 163 until a 2-dimensional profile of the transmembrane net driving force is produced. The spatially averaged transmembrane net driving force through membrane 102 would then be calculated by number averaging the transmembrane net driving forces at each point within the 2-dimensional profile.
According to certain embodiments, the transmembrane net driving force can be made uniform, at least in part, by initiating (and/or selecting) appropriate operating conditions (e.g., mass flow rates, osmotic pressures, and/or hydraulic pressures) at the feed inlet and the draw inlet to the osmotic separators, as described in more detail below.
Certain of the systems and methods described herein can be operated such that the conditions at the inlets on each side of the osmotic membrane satisfy the following equation:
m D , i m F , i = C π F , i - ( P F - P D ) π D , i + ( P F - P D ) [ 4 ]
wherein PF is the hydraulic pressure at the inlet of the feed stream (i.e., the stream entering the osmotic separator and from which water is removed during the osmosis process); mF,i is the mass flow rate of the feed stream at the inlet of the feed stream to the osmotic membrane; πF,i is the osmotic pressure of the feed stream at the inlet of the feed stream to the osmotic membrane; PD is the hydraulic pressure at the inlet of the draw stream to the osmotic membrane (i.e., the stream entering the osmotic separator and into which water is added during the osmosis process); mD,i is the mass flow rate of the draw stream at the inlet of the draw stream; πD,i is the osmotic pressure of the draw stream at the inlet of the draw stream; and C is from about 0.8 to about 1.2. In certain embodiments, C can be from about 0.9 to about 1.1, from about 0.95 to about 1.05, from about 0.98 to about 1.02, or from about 0.99 to about 1.01. Without wishing to be bound by any particular theory, it is believed that operating osmotic membranes such that they satisfy Equation 4 above can reduce (e.g., minimize) entropy generation and establish substantially uniform local fluxes of water through the osmotic membrane, which can reduce the amount of energy wasted during the osmosis process.
For the purposes of evaluating the performance of a system with respect to Equation 4, the mass flow rates, hydraulic pressures, and osmotic pressures of incoming streams should be measured as bulk mass flow rates, bulk hydraulic pressures, and bulk osmotic pressures of the incoming liquids at their point of entry to the osmotic separator. Bulk hydraulic pressure (which is generally measured as a gauge pressure) can be measured, for example, using a pressure transducer, a Bourdon tube, a diaphragm pressure gauge, or any other suitable pressure gauge. Mass flow rates may be determined using any of a number of suitable flow meters known to those of ordinary skill in the art. The bulk osmotic pressure of a stream may be determined, for example, by measuring the osmotic pressure (e.g., using any of the methods described elsewhere herein) of a sample of the stream.
Referring to FIG. 1B, for example, in certain embodiments, the osmotic separator comprising osmotic membrane 102 can be operated such that:
m 110 m 108 = C π 108 - ( P 108 - P 110 ) π 110 + ( P 108 - P 110 ) [ 4 A ]
wherein P108 is the bulk hydraulic pressure of stream 108 as it enters the osmotic separator; m108 is the bulk mass flow rate of stream 108 as it enters the osmotic separator; π108 is the bulk osmotic pressure of stream 108 as it enters the osmotic separator; P110 is the bulk hydraulic pressure of stream 110 as it enters the osmotic separator; m110 is the bulk mass flow rate of stream 110 as it enters the osmotic separator; π110 is the bulk osmotic pressure of stream 110 as it enters the osmotic separator; and C is from about 0.8 to about 1.2. In certain embodiments, C can be from about 0.9 to about 1.1, from about 0.95 to about 1.05, from about 0.98 to about 1.02, or from about 0.99 to about 1.01.
As one non-limiting example, in certain embodiments, the first osmotic separator (comprising the first osmotic membrane) can be operated such that it satisfies Equation 4 above. For example, in some embodiments, referring to FIGS. 2A-2B, the first osmotic separator comprising first osmotic membrane 202 can be operated such that:
m 210 m 208 = C π 208 - ( P 208 - P 210 ) π 210 + ( P 208 - P 210 ) [ 4 B ]
wherein P208 is the bulk hydraulic pressure of stream 208 as it enters the first osmotic separator; m208 is the bulk mass flow rate of stream 208 as it enters the first osmotic separator; π208 is the bulk osmotic pressure of stream 208 as it enters the first osmotic separator; P210 is the bulk hydraulic pressure of stream 210 as it enters the first osmotic separator; m210 is the bulk mass flow rate of stream 210 as it enters the first osmotic separator; π210 is the bulk osmotic pressure of stream 210 as it enters the first osmotic separator; and C is from about 0.8 to about 1.2. In certain embodiments, C can be from about 0.9 to about 1.1, from about 0.95 to about 1.05, from about 0.98 to about 1.02, or from about 0.99 to about 1.01.
In some embodiments, the second osmotic separator (comprising the second osmotic membrane) can be operated such that it satisfies Equation 4 above. For example, in some embodiments, referring to FIGS. 2A-2B, the second osmotic separator comprising second osmotic membrane 216 can be operated such that:
m 222 m 212 = C π 212 - ( P 212 - P 222 ) π 222 + ( P 212 - P 222 ) [ 4 C ]
wherein P212 is the bulk hydraulic pressure of stream 212 as it enters the second osmotic separator; m212 is the bulk mass flow rate of stream 212 as it enters the second osmotic separator; π212 is the bulk osmotic pressure of stream 212 as it enters the second osmotic separator; P222 is the bulk hydraulic pressure of stream 222 as it enters the second osmotic separator; m222 is the bulk mass flow rate of stream 222 as it enters the second osmotic separator; π222 is the bulk osmotic pressure of stream 222 as it enters the second osmotic separator; and C is from about 0.8 to about 1.2. In certain embodiments, C can be from about 0.9 to about 1.1, from about 0.95 to about 1.05, from about 0.98 to about 1.02, or from about 0.99 to about 1.01.
According to certain embodiments, the third osmotic separator (comprising the third osmotic membrane) can be operated such that it satisfies Equation 4 above. For example, in some embodiments, referring to FIG. 2B, the third osmotic separator comprising third osmotic membrane 228 can be operated such that:
m 234 m 224 = C π 224 - ( P 224 - P 234 ) π 234 + ( P 224 - P 234 ) [ 4 D ]
wherein P224 is the bulk hydraulic pressure of stream 224 as it enters the third osmotic separator; m224 is the bulk mass flow rate of stream 224 as it enters the third osmotic separator; π224 is the bulk osmotic pressure of stream 224 as it enters the third osmotic separator; P234 is the bulk hydraulic pressure of stream 234 as it enters the third osmotic separator; m234 is the bulk mass flow rate of stream 234 as it enters the third osmotic separator; π234 is the bulk osmotic pressure of stream 234 as it enters the third osmotic separator; and C is from about 0.8 to about 1.2. In certain embodiments, C can be from about 0.9 to about 1.1, from about 0.95 to about 1.05, from about 0.98 to about 1.02, or from about 0.99 to about 1.01.
According to certain embodiments, the fourth osmotic separator (comprising the fourth osmotic membrane) can be operated such that it satisfies Equation 4 above. For example, in some embodiments, referring to FIG. 2B, the fourth osmotic separator comprising fourth osmotic membrane 240 can be operated such that:
m 246 m 236 = C π 236 - ( P 236 - P 246 ) π 246 + ( P 236 - P 246 ) [ 4 E ]
wherein P236 is the bulk hydraulic pressure of stream 236 as it enters the fourth osmotic separator; m236 is the bulk mass flow rate of stream 236 as it enters the fourth osmotic separator; π236 is the bulk osmotic pressure of stream 236 as it enters the fourth osmotic separator; P246 is the bulk hydraulic pressure of stream 246 as it enters the fourth osmotic separator; m246 is the bulk mass flow rate of stream 246 as it enters the fourth osmotic separator; π246 is the bulk osmotic pressure of stream 246 as it enters the fourth osmotic separator; and C is from about 0.8 to about 1.2. In certain embodiments, C can be from about 0.9 to about 1.1, from about 0.95 to about 1.05, from about 0.98 to about 1.02, or from about 0.99 to about 1.01.
Certain embodiments comprise directing the transport of an aqueous feed stream across an osmotic membrane and/or a draw inlet stream across an osmotic membrane such that the following two ratios are within about 20% of each other (and/or, in some embodiments, within about 10% of each other, within about 5% of each other, within about 3% of each other, within about 2% of each other, or within about 1% of each other): a ratio of a mass flow rate of the draw inlet stream entering the osmotic membrane to a mass flow rate of the aqueous feed stream entering the osmotic membrane; and a ratio of the difference between the osmotic pressure of the aqueous feed stream entering the osmotic membrane and the inlet pressure difference across the osmotic membrane to the sum of the osmotic pressure of the draw inlet stream entering the osmotic membrane and the inlet pressure difference across the osmotic membrane. The inlet pressure difference across an osmotic membrane corresponds to the difference between the hydraulic pressure at the inlet of the feed stream (also referred to herein as PF) and the hydraulic pressure at the inlet of the draw stream to the osmotic membrane (also referred to herein as PD). The inlet pressure difference across an osmotic membrane can, thus, be expressed as PF−PD.
The ratio of a mass flow rate of the draw inlet stream entering the osmotic membrane (also referred to herein as mD,i) to a mass flow rate of the aqueous feed stream entering the osmotic membrane (also referred to herein as mF,i) can be calculated by dividing the mass flow rate of the draw inlet stream entering the osmotic membrane by the mass flow rate of the aqueous feed stream entering the osmotic membrane (and, thus, may be expressed as mD,i/mF,i). Similarly, ratio of the difference between the osmotic pressure of the aqueous feed stream entering the osmotic membrane and the inlet pressure difference across the osmotic membrane (also referred to herein as πF,i−(PF−PD)) to the sum of the osmotic pressure of the draw inlet stream entering the osmotic membrane and the inlet pressure difference across the osmotic membrane (also referred to herein as πD,i+(PF−PD)) can be calculated by dividing the difference between the osmotic pressure of the aqueous feed stream entering the osmotic membrane and the inlet pressure difference across the osmotic membrane by the sum of the osmotic pressure of the draw inlet stream entering the osmotic membrane and the inlet pressure difference across the osmotic membrane (and, thus, may be expressed as [(πF,I−(PF−PD))/(πD,I+(PF−PD))]. For the purposes of evaluating the ratios outlined above, the mass flow rates, hydraulic pressures, and osmotic pressures of incoming streams should be measured as bulk mass flow rates, bulk hydraulic pressures, and bulk osmotic pressures of the incoming liquids at their place of entry to the osmotic separator.
Referring to FIG. 1B, for example, certain embodiments comprise directing the transport of aqueous feed stream 108 across osmotic membrane 102 and/or draw inlet stream 110 across osmotic membrane 102 such that the following two ratios are within 20% of each other (and/or, in some embodiments, within about 10% of each other, within about 5% of each other, within about 3% of each other, within about 2% of each other, or within about 1% of each other): the ratio of the mass flow rate of draw inlet stream 110 entering osmotic membrane 102 to the mass flow rate of aqueous feed stream 108 entering osmotic membrane 102; and the ratio of the difference between the osmotic pressure of aqueous feed stream 108 entering osmotic membrane 102 and the inlet pressure difference across osmotic membrane 102 to the sum of the osmotic pressure of draw inlet stream 110 entering osmotic membrane 102 and the inlet pressure difference across osmotic membrane 102. The inlet pressure difference across osmotic membrane 102 can be determined by subtracting the hydraulic pressure of draw inlet stream 110 at the inlet of draw inlet stream 110 to osmotic membrane 102 from the hydraulic pressure of aqueous feed stream 108 at the inlet of aqueous feed stream 108 to osmotic membrane 102.
In certain embodiments, the first osmotic separator (comprising the first osmotic membrane) can be operated such that the ratios described above are relatively close to each other. For example, referring to FIGS. 2A-2B, certain embodiments comprise directing the transport of aqueous feed stream 208 across first osmotic membrane 202 and/or first draw inlet stream 210 across first osmotic membrane 202 such that the following two ratios are within 20% of each other (and/or, in some embodiments, within about 10% of each other, within about 5% of each other, within about 3% of each other, within about 2% of each other, or within about 1% of each other): the ratio of the mass flow rate of first draw inlet stream 210 entering first osmotic membrane 202 to the mass flow rate of aqueous feed stream 208 entering first osmotic membrane 202; and the ratio of the difference between the osmotic pressure of aqueous feed stream 208 entering first osmotic membrane 202 and the inlet pressure difference across first osmotic membrane 202 to the sum of the osmotic pressure of first draw inlet stream 210 entering first osmotic membrane 202 and the inlet pressure difference across first osmotic membrane 202. The inlet pressure difference across first osmotic membrane 202 can be determined by subtracting the hydraulic pressure of first draw inlet stream 210 at the inlet of first draw inlet stream 210 to first osmotic membrane 202 from the hydraulic pressure of aqueous feed stream 208 at the inlet of aqueous feed stream 208 to first osmotic membrane 202.
In certain embodiments, the second osmotic separator (comprising the second osmotic membrane) can be operated such that the ratios described above are relatively close to each other. For example, referring to FIGS. 2A-2B, certain embodiments comprise directing the transport of first draw product stream 212 across second osmotic membrane 216 and/or second draw inlet stream 222 across second osmotic membrane 216 such that the following two ratios are within 20% of each other (and/or, in some embodiments, within about 10% of each other, within about 5% of each other, within about 3% of each other, within about 2% of each other, or within about 1% of each other): the ratio of the mass flow rate of second draw inlet stream 222 entering second osmotic membrane 216 to the mass flow rate of first draw product stream 212 entering second osmotic membrane 216; and the ratio of the difference between the osmotic pressure of first draw product stream 212 entering second osmotic membrane 216 and the inlet pressure difference across second osmotic membrane 216 to the sum of the osmotic pressure of second draw inlet stream 222 entering second osmotic membrane 216 and the inlet pressure difference across second osmotic membrane 216. The inlet pressure difference across second osmotic membrane 216 can be determined by subtracting the hydraulic pressure of second draw inlet stream 222 at the inlet of second draw inlet stream 222 to second osmotic membrane 216 from the hydraulic pressure of first draw product stream 212 at the inlet of first draw product stream 212 to second osmotic membrane 216.
In certain embodiments, the third osmotic separator (comprising the third osmotic membrane) can be operated such that the ratios described above are relatively close to each other. For example, referring to FIG. 2B, certain embodiments comprise directing the transport of second draw product stream 224 across third osmotic membrane 228 and/or third draw inlet stream 234 across third osmotic membrane 228 such that the following two ratios are within 20% of each other (and/or, in some embodiments, within about 10% of each other, within about 5% of each other, within about 3% of each other, within about 2% of each other, or within about 1% of each other): the ratio of the mass flow rate of third draw inlet stream 234 entering third osmotic membrane 228 to the mass flow rate of second draw product stream 224 entering third osmotic membrane 228; and the ratio of the difference between the osmotic pressure of second draw product stream 224 entering third osmotic membrane 228 and the inlet pressure difference across third osmotic membrane 228 to the sum of the osmotic pressure of third draw inlet stream 234 entering third osmotic membrane 228 and the inlet pressure difference across third osmotic membrane 228. The inlet pressure difference across third osmotic membrane 228 can be determined by subtracting the hydraulic pressure of third draw inlet stream 234 at the inlet of third draw inlet stream 234 to third osmotic membrane 228 from the hydraulic pressure of second draw product stream 224 at the inlet of second draw product stream 224 to third osmotic membrane 228.
In certain embodiments, the fourth osmotic separator (comprising the fourth osmotic membrane) can be operated such that the ratios described above are relatively close to each other. For example, referring to FIG. 2B, certain embodiments comprise directing the transport of third draw product stream 236 across third osmotic membrane 240 and/or fourth draw inlet stream 246 across fourth osmotic membrane 240 such that the following two ratios are within 20% of each other (and/or, in some embodiments, within about 10% of each other, within about 5% of each other, within about 3% of each other, within about 2% of each other, or within about 1% of each other): the ratio of the mass flow rate of fourth draw inlet stream 246 entering fourth osmotic membrane 240 to the mass flow rate of third draw product stream 236 entering fourth osmotic membrane 240; and the ratio of the difference between the osmotic pressure of third draw product stream 236 entering fourth osmotic membrane 240 and the inlet pressure difference across fourth osmotic membrane 240 to the sum of the osmotic pressure of fourth draw inlet stream 246 entering fourth osmotic membrane 240 and the inlet pressure difference across fourth osmotic membrane 240. The inlet pressure difference across fourth osmotic membrane 240 can be determined by subtracting the hydraulic pressure of fourth draw inlet stream 246 at the inlet of fourth draw inlet stream 246 to fourth osmotic membrane 240 from the hydraulic pressure of third draw product stream 236 at the inlet of third draw product stream 236 to fourth osmotic membrane 240.
Certain embodiments comprise directing the transport of an aqueous feed stream across an osmotic membrane and/or a draw inlet stream across the osmotic membrane such that the transmembrane net driving force at the entrance of the aqueous feed stream to the osmotic membrane and the transmembrane net driving force at the entrance of the draw inlet stream to the osmotic membrane are within about 10% of each other (and/or, in some embodiments, within about 5% of each other, within about 3% of each other, within about 2% of each other, or within about 1% of each other). The transmembrane net driving force at a particular location along an osmotic membrane can be calculated using Equation 1, as described above.
Referring to FIG. 1B, for example, certain embodiments comprise directing the transport of aqueous feed stream 108 across osmotic membrane 102 and/or draw inlet stream 110 across osmotic membrane 102 such that the transmembrane net driving force at the entrance of aqueous feed stream 108 to osmotic membrane 102 and the transmembrane net driving force at the entrance of draw inlet stream 110 to osmotic membrane 102 are within about 10% of each other (and/or, in some embodiments, within about 5% of each other, within about 3% of each other, within about 2% of each other, or within about 1% of each other).
In certain embodiments, the first osmotic separator (comprising the first osmotic membrane) can be operated such that the transmembrane net driving forces at the inlets to the first osmotic membrane are relatively close to each other. For example, referring to FIGS. 2A-2B, certain embodiments comprise directing the transport of aqueous feed stream 208 across first osmotic membrane 202 and/or first draw inlet stream 210 across first osmotic membrane 202 such that the transmembrane net driving force at the entrance of aqueous feed stream 208 to first osmotic membrane 202 and the transmembrane net driving force at the entrance of first draw inlet stream 210 to first osmotic membrane 202 are within about 10% of each other (and/or, in some embodiments, within about 5% of each other, within about 3% of each other, within about 2% of each other, or within about 1% of each other).
In certain embodiments, the second osmotic separator (comprising the second osmotic membrane) can be operated such that the transmembrane net driving forces at the inlets to the second osmotic membrane are relatively close to each other. For example, referring to FIGS. 2A-2B, certain embodiments comprise directing the transport of first draw product stream 212 across second osmotic membrane 216 and/or second draw inlet stream 222 across second osmotic membrane 216 such that the transmembrane net driving force at the entrance of first draw product stream 212 to second osmotic membrane 216 and the transmembrane net driving force at the entrance of second draw inlet stream 222 to second osmotic membrane 216 are within about 10% of each other (and/or, in some embodiments, within about 5% of each other, within about 3% of each other, within about 2% of each other, or within about 1% of each other).
In certain embodiments, the third osmotic separator (comprising the third osmotic membrane) can be operated such that the transmembrane net driving forces at the inlets to the third osmotic membrane are relatively close to each other. For example, referring to FIG. 2B, certain embodiments comprise directing the transport of second draw product stream 224 across third osmotic membrane 228 and/or third draw inlet stream 234 across third osmotic membrane 228 such that the transmembrane net driving force at the entrance of second draw product stream 224 to third osmotic membrane 228 and the transmembrane net driving force at the entrance of third draw inlet stream 234 to third osmotic membrane 228 are within about 10% of each other (and/or, in some embodiments, within about 5% of each other, within about 3% of each other, within about 2% of each other, or within about 1% of each other).
In certain embodiments, the fourth osmotic separator (comprising the fourth osmotic membrane) can be operated such that the transmembrane net driving forces at the inlets to the fourth osmotic membrane are relatively close to each other. For example, referring to FIG. 2B, certain embodiments comprise directing the transport of third draw product stream 236 across fourth osmotic membrane 240 and/or fourth draw inlet stream 246 across fourth osmotic membrane 240 such that the transmembrane net driving force at the entrance of third draw product stream 236 to fourth osmotic membrane 240 and the transmembrane net driving force at the entrance of fourth draw inlet stream 246 to fourth osmotic membrane 240 are within about 10% of each other (and/or, in some embodiments, within about 5% of each other, within about 3% of each other, within about 2% of each other, or within about 1% of each other).
The transmembrane net driving force at the inlet(s) to an osmotic membrane can be controlled, initiated, and/or selected, for example, by selecting appropriate operating conditions (e.g., mass flow rates, osmotic pressures (e.g., via solubilized species selection and/or concentration), and/or hydraulic pressures) of the flow streams.
In some embodiments, one or more osmotic membranes can be operated such that the transmembrane net driving forces at the inlets to the osmotic membrane are initially relatively unbalanced, after which, operation of the system may be adjusted such that the transmembrane net driving forces at the inlets to the osmotic membrane are relatively balanced. For example, some embodiments comprise directing the transport of the aqueous feed stream across the osmotic membrane and/or the draw inlet stream across the osmotic membrane such that the transmembrane net driving force at the entrance of the aqueous feed stream to the osmotic membrane and the transmembrane net driving force at the entrance of the draw inlet stream to the osmotic membrane are at least about 10% different from each other (and/or, in some embodiments, at least about 11%, at least about 12%, at least about 15%, at least about 20%, at least about 50%, or at least about 100% different from each other). Some such embodiments comprise measuring at least one of a temperature, a pressure, a solubilized species concentration, and a flow rate of the aqueous feed stream and/or the draw inlet stream. Some such embodiments comprise changing at least one of the flow rate of the aqueous feed stream and the flow rate of the draw inlet stream such that the transmembrane driving force at the entrance of the aqueous feed stream to the osmotic membrane and the transmembrane driving force at the entrance of the draw inlet stream to the osmotic membrane are within about 10% of each other (and/or, in some embodiments, within about 5%, within about 3%, within about 2%, or within about 1% of each other).
Referring to FIG. 1B, for example, certain embodiments comprise directing the transport of aqueous feed stream 108 across osmotic membrane 102 and/or draw inlet stream 110 across osmotic membrane 102 such that the transmembrane net driving force at the entrance of aqueous feed stream 108 to osmotic membrane 102 and the transmembrane driving force at the entrance of draw inlet stream 110 to osmotic membrane 102 are at least about 10% different from each other (and/or, in some embodiments, at least about 11%, at least about 12%, at least about 15%, at least about 20%, at least about 50%, or at least about 100% different from each other). Some such embodiments comprise measuring at least one of a temperature, a pressure, a solubilized species concentration, and a flow rate of aqueous feed stream 108 and/or draw inlet stream 110. Some such embodiments comprise changing at least one of the flow rate of aqueous feed stream 108 and the flow rate of draw inlet stream 110 such that the transmembrane driving force at the entrance of aqueous feed stream 108 to osmotic membrane 102 and the transmembrane driving force at the entrance of draw inlet stream 110 to osmotic membrane 102 are within about 10% of each other (and/or, in some embodiments, within about 5%, within about 3%, within about 2%, or within about 1% of each other).
In certain embodiments, the first osmotic separator (comprising the first osmotic membrane) can be operated such that the transmembrane net driving forces at the inlets to the first osmotic membrane are initially relatively unbalanced, after which, operation of the system may be adjusted such that the transmembrane net driving forces at the inlets to the first osmotic membrane are relatively balanced. For example, referring to FIGS. 2A-2B, certain embodiments comprise directing the transport of aqueous feed stream 208 across first osmotic membrane 202 and/or first draw inlet stream 210 across first osmotic membrane 202 such that the transmembrane net driving force at the entrance of aqueous feed stream 208 to first osmotic membrane 202 and the transmembrane driving force at the entrance of first draw inlet stream 210 to first osmotic membrane 202 are at least about 10% different from each other (and/or, in some embodiments, at least about 11%, at least about 12%, at least about 15%, at least about 20%, at least about 50%, or at least about 100% different from each other). Some such embodiments comprise measuring at least one of a temperature, a pressure, a solubilized species concentration, and a flow rate of aqueous feed stream 208 and/or first draw inlet stream 210. Some such embodiments comprise changing at least one of the flow rate of aqueous feed stream 208 and the flow rate of first draw inlet stream 210 such that the transmembrane driving force at the entrance of aqueous feed stream 208 to first osmotic membrane 202 and the transmembrane driving force at the entrance of first draw inlet stream 210 to first osmotic membrane 202 are within about 10% of each other (and/or, in some embodiments, within about 5%, within about 3%, within about 2%, or within about 1% of each other).
In certain embodiments, the second osmotic separator (comprising the second osmotic membrane) can be operated such that the transmembrane net driving forces at the inlets to the second osmotic membrane are initially relatively unbalanced, after which, operation of the system may be adjusted such that the transmembrane net driving forces at the inlets to the second osmotic membrane are relatively balanced. For example, referring to FIGS. 2A-2B, certain embodiments comprise directing the transport of first draw product stream 212 across second osmotic membrane 216 and/or second draw inlet stream 222 across second osmotic membrane 216 such that the transmembrane net driving force at the entrance of first draw product stream 212 to second osmotic membrane 216 and the transmembrane driving force at the entrance of second draw inlet stream 222 to second osmotic membrane 216 are at least about 10% different from each other (and/or, in some embodiments, at least about 11%, at least about 12%, at least about 15%, at least about 20%, at least about 50%, or at least about 100% different from each other). Some such embodiments comprise measuring at least one of a temperature, a pressure, a solubilized species concentration, and a flow rate of first draw product stream 212 and/or second draw inlet stream 222. Some such embodiments comprise changing at least one of the flow rate of first draw product stream 212 and the flow rate of second draw inlet stream 222 such that the transmembrane driving force at the entrance of first draw product stream 212 to second osmotic membrane 216 and the transmembrane driving force at the entrance of second draw inlet stream 222 to second osmotic membrane 216 are within about 10% of each other (and/or, in some embodiments, within about 5%, within about 3%, within about 2%, or within about 1% of each other).
In certain embodiments, the third osmotic separator (comprising the third osmotic membrane) can be operated such that the transmembrane net driving forces at the inlets to the third osmotic membrane are initially relatively unbalanced, after which, operation of the system may be adjusted such that the transmembrane net driving forces at the inlets to the third osmotic membrane are relatively balanced. For example, referring to FIG. 2B, certain embodiments comprise directing the transport of second draw product stream 224 across third osmotic membrane 228 and/or third draw inlet stream 234 across third osmotic membrane 228 such that the transmembrane net driving force at the entrance of second draw product stream 224 to third osmotic membrane 228 and the transmembrane driving force at the entrance of third draw inlet stream 234 to third osmotic membrane 228 are at least about 10% different from each other (and/or, in some embodiments, at least about 11%, at least about 12%, at least about 15%, at least about 20%, at least about 50%, or at least about 100% different from each other). Some such embodiments comprise measuring at least one of a temperature, a pressure, a solubilized species concentration, and a flow rate of second draw product stream 224 and/or third draw inlet stream 234. Some such embodiments comprise changing at least one of the flow rate of second draw product stream 224 and the flow rate of third draw inlet stream 234 such that the transmembrane driving force at the entrance of second draw product stream 224 to third osmotic membrane 228 and the transmembrane driving force at the entrance of third draw inlet stream 234 to third osmotic membrane 228 are within about 10% of each other (and/or, in some embodiments, within about 5%, within about 3%, within about 2%, or within about 1% of each other).
In certain embodiments, the fourth osmotic separator (comprising the fourth osmotic membrane) can be operated such that the transmembrane net driving forces at the inlets to the fourth osmotic membrane are initially relatively unbalanced, after which, operation of the system may be adjusted such that the transmembrane net driving forces at the inlets to the fourth osmotic membrane are relatively balanced. For example, referring to FIG. 2B, certain embodiments comprise directing the transport of third draw product stream 236 across fourth osmotic membrane 240 and/or fourth draw inlet stream 246 across fourth osmotic membrane 240 such that the transmembrane net driving force at the entrance of third draw product stream 236 to fourth osmotic membrane 240 and the transmembrane driving force at the entrance of fourth draw inlet stream 246 to fourth osmotic membrane 240 are at least about 10% different from each other (and/or, in some embodiments, at least about 11%, at least about 12%, at least about 15%, at least about 20%, at least about 50%, or at least about 100% different from each other). Some such embodiments comprise measuring at least one of a temperature, a pressure, a solubilized species concentration, and a flow rate of third draw product stream 236 and/or fourth draw inlet stream 246. Some such embodiments comprise changing at least one of the flow rate of third draw product stream 236 and the flow rate of fourth draw inlet stream 246 such that the transmembrane driving force at the entrance of third draw product stream 236 to fourth osmotic membrane 240 and the transmembrane driving force at the entrance of fourth draw inlet stream 246 to fourth osmotic membrane 240 are within about 10% of each other (and/or, in some embodiments, within about 5%, within about 3%, within about 2%, or within about 1% of each other).
Certain of the systems and methods described herein can be employed such that, during operation, for at least one of the osmotic membranes (e.g., at least one of the first osmotic membrane, the second osmotic membrane, the third osmotic membrane, the fourth osmotic membrane, etc.), the linear flow rate of water through the thickness of the osmotic membrane (i.e., the transmembrane linear flow rate of water) is spatially uniform across the facial area of the osmotic membrane. One of ordinary skill in the art would be capable of determining the transmembrane linear flow rate of water at various points across the facial area of the osmotic membrane during operation, for example, by measuring concentrations of streams on each side of the osmotic membrane at various locations and performing a mass balance on the osmotic membrane. In some embodiments, over at least about 90%, at least about 95%, at least about 98%, or at least about 99% of the facial area of the osmotic membrane (e.g., the first osmotic membrane, the second osmotic membrane, the third osmotic membrane (if present), and/or the fourth osmotic membrane (if present)), the transmembrane linear flow rate of water is uniform to within about 20%, within about 10%, within about 5%, within about 3%, within about 2%, or within about 1%. To determine the percentage of facial area over which the transmembrane linear flow rate of water is spatially uniform, one would use a similar procedure as described above with respect to the uniformity of the transmembrane net driving force. For example, one would determine the transmembrane linear flow rates of water at points across the two-dimensional facial area of the osmotic membrane (e.g., at points across facial area 163 shown in FIG. 1C, defined by dimensions 160 and 161). The transmembrane linear flow rate of water at a particular location on the osmotic membrane would be said to be uniform to within X % if the transmembrane linear flow rate of water at that location is within X % of the spatially-averaged transmembrane linear flow rate of water. To determine the spatially-averaged transmembrane linear flow rate of water, one would determine the transmembrane linear flow rate of water at each point across the facial area of the osmotic membrane (to produce a two-dimensional distribution) and spatially average the distribution of the transmembrane linear flow rates of water. Without wishing to be bound by any particular theory, it is believed that operation of one or more osmotic membranes such that the linear flow rate of water is relatively spatially uniform across the membrane can produce relatively uniform water flux across the facial area of the membrane, which can lead to reductions in thermodynamic losses during operation of the membrane.
According to certain embodiments, the streams on either side of an osmotic membrane can be operated in counter-current configuration. Operation of the desalination system in this manner can, according to certain but not necessarily all embodiments, allow one to more easily ensure that the transmembrane net driving force is spatially uniform across the facial area of the osmotic membrane. An example of counter-current flow is illustrated in FIG. 1B, in which aqueous feed stream 108 is transported across first side 104 of osmotic membrane 102 in the direction of arrow 103 while draw inlet stream 110 is transported across second side 106 of osmotic membrane 102 in the direction of arrow 105. It should be understood that two streams do not have to be transported in perfectly parallel and opposite directions to be considered to be in counter-current configuration, and in some embodiments, the primary flow directions of two streams that are in a counter-current flow configuration can form an angle of up to about 10° (or, in some cases, up to about 5°, up to about 2°, or up to about 10). In certain embodiments, the aqueous feed stream and the first draw inlet stream are transported across the first osmotic membrane in a counter-current configuration. According to some embodiments, the first draw product stream and the second draw inlet stream are transported across the second osmotic membrane in a counter-current configuration. In some embodiments, the second draw product stream and the third draw inlet stream are transported across the third osmotic membrane in a counter-current configuration. In some embodiments, the third draw product stream and the fourth draw inlet stream are transported across the fourth osmotic membrane in a counter-current configuration.
According to certain embodiments, streams within the desalination system can be recycled. For example, in certain embodiments, at least a portion of the second concentrated aqueous stream is recycled to the second side of the first osmotic membrane. In some embodiments, the first draw inlet stream contains at least a portion of the second concentrated aqueous stream. For example, in FIGS. 2A-2B, at least a portion of stream 226 can be recycled to second side 206 of osmotic membrane 202, in some embodiments. In some such cases, first draw inlet stream 210 can contain at least a portion of second concentrated aqueous stream 226, as indicated by the dotted line connecting streams 226 and 210. In some embodiments, at least a portion of the third concentrated aqueous stream is recycled to the second side of the second osmotic membrane. In some embodiments, the second draw inlet stream contains at least a portion of the third concentrated aqueous stream. For example, in FIG. 2B, at least a portion of stream 238 can be recycled to second side 220 of osmotic membrane 216, in some embodiments. In some such cases, second draw inlet stream 222 can contain at least a portion of third concentrated aqueous stream 238, as indicated by the dotted line connecting streams 238 and 222. In some embodiments, at least a portion of the fourth concentrated aqueous stream is recycled to the second side of the third osmotic membrane. In some embodiments, the third draw inlet stream contains at least a portion of the fourth concentrated aqueous stream. For example, in FIG. 2B, at least a portion of stream 250 can be recycled to second side 232 of osmotic membrane 228, in some embodiments. In some such cases, third draw inlet stream 234 can contain at least a portion of fourth concentrated aqueous stream 250, as indicated by the dotted line connecting streams 250 and 234. Recycling of the streams in this manner can, according to certain although not necessarily all embodiments, simplify operation of the desalination system, reduce the volume of waste generated by the desalination system, and allow steady-state operation to be achieved more easily.
One advantage of certain, although not necessarily all, embodiments is that one or more of the osmotic-membrane-based desalination steps can be performed to achieve a desired degree of desalination while using relatively low transmembrane osmotic pressure gradients. Such low transmembrane osmotic pressure gradients can be advantageous, for example, in certain cases in which reverse osmosis is used to perform desalination, as relatively low transmembrane osmotic pressure gradients can allow one to perform separations using relatively low applied hydraulic pressures, thus potentially reducing energy requirements and/or equipment costs compared to higher hydraulic pressure applications. In some embodiments, at at least one location on the first osmotic membrane, the difference between an osmotic pressure on a first side of the first osmotic membrane and an osmotic pressure on a second side of the first osmotic membrane (i.e., opposite the first side of the first osmotic membrane) is less than about 45 bar, less than about 40 bar, less than about 35 bar, less than about 30 bar, less than about 25 bar, less than about 20 bar, or less (and/or, in some embodiments, at least about 1 bar, at least about 2 bar, at least about 5 bar, at least about 10 bar, or more). For example, in FIGS. 2A-2B, in some embodiments, at at least one location on first osmotic membrane 210, the difference between an osmotic pressure on first side 204 of first osmotic membrane 202 and an osmotic pressure on second side 206 of first osmotic membrane 202 is less than about 45 bar, less than about 40 bar, less than about 35 bar, less than about 30 bar, less than about 25 bar, less than about 20 bar, or less (and/or, in some embodiments, at least about 1 bar, at least about 2 bar, at least about 5 bar, at least about 10 bar, or more).
Relatively low transmembrane osmotic pressure gradients can also be present, in some embodiments, across the second, third, fourth, and/or additional osmotic membranes. For example, in some embodiments, at at least one location on the second osmotic membrane, the difference between the osmotic pressure on a first side of the second osmotic membrane and an osmotic pressure on a second side of the second osmotic membrane is less than about 45 bar, less than about 40 bar, less than about 35 bar, less than about 30 bar, less than about 25 bar, less than about 20 bar, or less (and/or, in some embodiments, at least about 1 bar, at least about 2 bar, at least about 5 bar, at least about 10 bar, or more). For example, in FIGS. 2A-2B, in some embodiments, at at least one location on second osmotic membrane 216, the difference between an osmotic pressure on first side 218 of second osmotic membrane 216 and an osmotic pressure on second side 220 of second osmotic membrane 216 is less than about 45 bar, less than about 40 bar, less than about 35 bar, less than about 30 bar, less than about 25 bar, less than about 20 bar, or less (and/or, in some embodiments, at least about 1 bar, at least about 2 bar, at least about 5 bar, at least about 10 bar, or more). In certain embodiments, at at least one location on the third osmotic membrane, the difference between the osmotic pressure on a first side of the third osmotic membrane and an osmotic pressure on a second side of the third osmotic membrane is less than about 45 bar, less than about 40 bar, less than about 35 bar, less than about 30 bar, less than about 25 bar, less than about 20 bar, or less (and/or, in some embodiments, at least about 1 bar, at least about 2 bar, at least about 5 bar, at least about 10 bar, or more). For example, in FIG. 2B, in some embodiments, at at least one location on third osmotic membrane 228, the difference between an osmotic pressure on first side 230 of third osmotic membrane 228 and an osmotic pressure on second side 232 of third osmotic membrane 228 is less than about 45 bar, less than about 40 bar, less than about 35 bar, less than about 30 bar, less than about 25 bar, less than about 20 bar, or less (and/or, in some embodiments, at least about 1 bar, at least about 2 bar, at least about 5 bar, at least about 10 bar, or more). In certain embodiments, at at least one location on the fourth osmotic membrane, the difference between the osmotic pressure on a first side of the fourth osmotic membrane and an osmotic pressure on a second side of the fourth osmotic membrane is less than about 45 bar, less than about 40 bar, less than about 35 bar, less than about 30 bar, less than about 25 bar, less than about 20 bar, or less (and/or, in some embodiments, at least about 1 bar, at least about 2 bar, at least about 5 bar, at least about 10 bar, or more). For example, in FIG. 2B, in some embodiments, at at least one location on fourth osmotic membrane 240, the difference between an osmotic pressure on first side 242 of fourth osmotic membrane 240 and an osmotic pressure on second side 244 of fourth osmotic membrane 240 is less than about 45 bar, less than about 40 bar, less than about 35 bar, less than about 30 bar, less than about 25 bar, less than about 20 bar, or less (and/or, in some embodiments, at least about 1 bar, at least about 2 bar, at least about 5 bar, at least about 10 bar, or more).
According to certain embodiments, the transmembrane osmotic pressure gradient spatially-averaged across the facial area of one or more of the osmotic membranes (e.g., the first osmotic membrane such as membrane 202 in FIGS. 2A-2B, the second osmotic membrane such as membrane 216 in FIGS. 2A-2B, the third osmotic membrane such as membrane 228 in FIG. 2B, and/or the fourth osmotic membrane such as membrane 240 in FIG. 2B) is relatively small. The spatially-averaged transmembrane osmotic pressure gradient across a facial area of a particular osmotic membrane can be calculated using a similar methodology as the calculation of the spatially-averaged transmembrane net driving force described above. For example, one can measure the osmotic pressure at all points along the facial area of the first side of the osmotic membrane, measure the osmotic pressure at all points along the facial area of the second side of the osmotic membrane, and calculate the two-dimensional distribution (across the facial area of the membrane) of the transmembrane osmotic pressure gradient (by subtracting, at each point across the facial area of the osmotic membrane, the osmotic pressure on the second side of the osmotic membrane from the osmotic pressure on the opposite point on the first side of the osmotic membrane). One can then spatially average the two-dimensional distribution of the transmembrane osmotic pressure gradient. To illustrate an exemplary calculation of the spatially-averaged transmembrane osmotic pressure gradient, reference is made to FIGS. 1C-1D. To determine the spatially-averaged transmembrane osmotic pressure gradient across facial area 163 of membrane 102 in FIGS. 1C-1D, one would calculate the two-dimensional distribution of the transmembrane osmotic pressure gradient (i.e., (Π1−Π2)) at each point across facial area 163 of osmotic membrane 102. At each point along the facial area of the osmotic membrane, the osmotic pressures would be determined at a point on a first side of the osmotic membrane and a corresponding, opposite point on the second side of the osmotic membrane. For example, in FIGS. 1C-1D, transmembrane osmotic pressure gradients would be determined between points 150A and 152A, between points 150B and 152B, between points 150C and 152C, between points 150D and 152D, between points 150E and 152E, and at a statistically representative number of point pairs across facial area 163 until a 2-dimensional profile of the transmembrane osmotic pressure gradient is produced. The spatially-averaged transmembrane osmotic pressure gradient across facial area 163 of membrane 102 would then be calculated by number averaging the transmembrane osmotic pressure gradients at each point within the 2-dimensional profile.
In certain embodiments, the transmembrane osmotic pressure gradient, spatially-averaged across the facial area of the membrane, for one or more of the osmotic membranes within the system (e.g., across the first osmotic membrane, the second osmotic membrane, the third osmotic membrane, and/or the fourth osmotic membrane) is less than about 45 bar, less than about 40 bar, less than about 35 bar, less than about 30 bar, less than about 25 bar, less than about 20 bar, or less (and/or, in some embodiments, at least about 1 bar, at least about 2 bar, at least about 5 bar, at least about 10 bar, or more).
Achieving a relatively low spatially-averaged transmembrane osmotic pressure gradient across a facial area of an osmotic membrane can be achieved, for example, by controlling the osmotic pressure of the streams fed to either side of the osmotic membrane (e.g., by controlling salt types and/or salt concentrations within the streams). According to certain embodiments, the difference between the osmotic pressure within the aqueous feed stream and the osmotic pressure within the first draw product stream is less than about 45 bar, less than about 40 bar, less than about 35 bar, less than about 30 bar, less than about 25 bar, less than about 20 bar, or less (and/or, in some embodiments, at least about 1 bar, at least about 2 bar, at least about 5 bar, at least about 10 bar, or more). In certain embodiments, the difference between the osmotic pressure of the first draw product stream and the osmotic pressure of the second draw product stream is less than about 45 bar, less than about 40 bar, less than about 35 bar, less than about 30 bar, less than about 25 bar, less than about 20 bar, or less (and/or, in some embodiments, at least about 1 bar, at least about 2 bar, at least about 5 bar, at least about 10 bar, or more). In some embodiments, the difference between the osmotic pressure of the second draw product stream and the osmotic pressure of the third draw product stream is less than about 45 bar, less than about 40 bar, less than about 35 bar, less than about 30 bar, less than about 25 bar, less than about 20 bar, or less (and/or, in some embodiments, at least about 1 bar, at least about 2 bar, at least about 5 bar, at least about 10 bar, or more).
In some embodiments, the transmembrane net driving forces from one osmotic membrane to another within the desalination system are relatively closely matched in magnitude. The use of similar transmembrane net driving forces from one osmotic membrane to another within the desalination system can allow one, according to certain embodiments, to perform desalination using applied pressures that are relatively closely matched in magnitude from membrane to membrane.
According to certain embodiments, the difference between the osmotic pressure of the first draw product stream and the osmotic pressure of the second draw inlet stream and the difference between the osmotic pressure of the second draw product stream and the osmotic pressure of the third draw inlet stream are within about 20%, within about 10%, within about 5%, within about 2%, or within about 1% of each other. For example, referring to FIG. 2B, in some embodiments, first draw product stream 212 can have an osmotic pressure (Π212) and second draw inlet stream 222 can have an osmotic pressure (Π212), such that the difference between the osmotic pressure within the first draw product stream and the osmotic pressure of the second draw inlet stream is calculated as Π212−Π222. In addition, second draw product stream 224 can have an osmotic pressure (Π224) and third draw inlet stream 234 can have an osmotic pressure (Π234), such that the difference between the osmotic pressure within the second draw product stream and the osmotic pressure of the third draw inlet stream is calculated as Π224−Π234. In some such embodiments, the difference between the osmotic pressure within the first draw product stream and the osmotic pressure of the second draw inlet stream (Π212−Π222) and the difference between the osmotic pressure within the second draw product stream and the osmotic pressure of the third draw inlet stream (Π224−Π234) are within about 20%, within about 10%, within about 5%, within about 2%, or within about 1% of each other.
According to certain embodiments, the difference between the osmotic pressure of the second draw product stream and the osmotic pressure of the third draw inlet stream and the difference between the osmotic pressure of the third draw product stream and the osmotic pressure of the fourth draw inlet stream are within about 20%, within about 10%, within about 5%, within about 2%, or within about 1% of each other. For example, referring to FIG. 2B, in some embodiments, second draw product stream 224 can have an osmotic pressure (Π224) and third draw inlet stream 234 can have an osmotic pressure (Π234), such that the difference between the osmotic pressure within the second draw product stream and the osmotic pressure of the third draw inlet stream is calculated as Π224−Π234. In addition, third draw product stream 236 can have an osmotic pressure (Π236) and fourth draw inlet stream 246 can have an osmotic pressure (Π246), such that the difference between the osmotic pressure within the third draw product stream and the osmotic pressure of the fourth draw inlet stream is calculated as Π236−Π246. In some such embodiments, the difference between the osmotic pressure of the second draw product stream and the osmotic pressure of the third draw inlet stream (Π224−Π234) and the difference between the osmotic pressure within the third draw product stream and the osmotic pressure of the fourth draw inlet stream (Π236−Π246) are within about 20%, within about 10%, within about 5%, within about 2%, or within about 1% of each other.
In some embodiments, the spatially-averaged transmembrane net driving force across the facial area of the second osmotic membrane and the spatially-averaged transmembrane net driving force across the facial area of the third osmotic membrane are within about 10%, within about 5%, within about 2%, or within about 1% of each other. In some embodiments, the spatially-averaged transmembrane net driving force across the facial area of the third osmotic membrane and the spatially-averaged transmembrane net driving force across the facial area of the fourth osmotic membrane are within about 10%, within about 5%, within about 2%, or within about 1% of each other.
When calculating the percentage difference between two values (unless specified otherwise herein), the percentage calculation is made using the value that is larger in magnitude as the basis. To illustrate, if a first value is V1, and a second value is V2 (which is larger than V1), the percentage difference (V% Diff) between V1 and V2 would be calculated as:
V % Diff = V 2 - V 1 V 2 × 100 % [ 5 ]
and the first and second values would be said to be within X % of each other if V% Diff is X % or less.
For example, if a first osmotic pressure difference (Δπ1) and a second osmotic pressure difference (Δπ2) are being compared, and the second osmotic pressure difference is larger in magnitude than the first osmotic pressure difference, the percentage difference (Δπ% Diff) would be calculated as:
Δπ % Diff = Δ π 2 - Δ π 1 Δ π 2 × 100 % [ 5 A ]
and the first and second osmotic pressure differences would be said to be within X % of each other if Δπ% Diff is X % or less.
In some embodiments, at least a portion of the energy used to pressurize one or more streams (e.g., for performing reverse osmosis) is recovered from the system. The recovered energy may be used, for example, to heat and/or pressurize another stream within the desalination system.
Some embodiments comprise, after transporting at least a portion of the first draw product stream from the second side of the first osmotic membrane across a first side of a second osmotic membrane, reducing a pressure of the portion of the first draw product stream transported across the first side of the second osmotic membrane. For example, referring to FIG. 2B, in some embodiments, after transporting at least a portion of first draw product stream 212 from the second side of first osmotic membrane 202 across first side 218 of second osmotic membrane 216, the pressure of second concentrated aqueous stream 226 can be reduced. In certain embodiments, after transporting at least a portion of the second draw product stream from the second side of the second osmotic membrane across a first side of a third osmotic membrane, the pressure of the portion of the second draw product stream transported across the first side of the third osmotic membrane is reduced. For example, referring to FIG. 2B, in some embodiments, after transporting at least a portion of second draw product stream 224 from the second side of second osmotic membrane 216 across first side 230 of third osmotic membrane 228, the pressure of third aqueous concentrated stream 238 can be reduced. In some embodiments, after transporting at least a portion of the third draw product stream from the second side of the third osmotic membrane across a first side of a fourth osmotic membrane, the pressure of the portion of the third draw product stream transported across the first side of the fourth osmotic membrane is reduced. For example, referring to FIG. 2B, in some embodiments, after transporting at least a portion of third draw product stream 236 from the second side of third osmotic membrane 228 across first side 242 of fourth osmotic membrane 240, the pressure of fourth concentrated aqueous stream 250 can be reduced.
Some embodiments comprise recovering at least a portion of the energy released by the reduction of the pressure of a stream that exits a retentate side of an osmotic membrane (e.g., any of the concentrated aqueous streams described elsewhere herein). For example, referring to FIGS. 2A-2B, some embodiments comprise recovering at least a portion of the energy released by the reduction of the pressure of concentrated aqueous stream 214, which exits first side 204 of osmotic membrane 202 (which is the retentate side of osmotic membrane 202), such as when first osmotic membrane 202 is used to perform pressure-assisted forward osmosis or reverse osmosis. As another example, certain embodiments comprise recovering at least a portion of the energy released by the reduction of the pressure of concentrated aqueous stream 226, which exits first side 218 of second osmotic membrane 216 (which is the retentate side of osmotic membrane 216). As yet another example, some embodiments comprise recovering at least a portion of the energy released by the reduction of pressure of third concentrated aqueous stream 238, which exits first side 230 of third osmotic membrane 228 (which is the retentate side of osmotic membrane 228). Some embodiments comprise recovering at least a portion of the energy released by the reduction of pressure of concentrated aqueous stream 250 which exits first side 242 of osmotic membrane 240 (which is the retentate side of osmotic membrane 240).
Certain embodiments comprise recovering at least a portion of the energy released by the reduction of the pressure of a draw product stream that has been transported across the retentate (first) side of an osmotic membrane.
According to some embodiments, at least a portion of the recovered energy may be used to increase the pressure of another stream in the system, which can reduce overall energy costs within the system. For example, the recovered energy can be used, according to certain embodiments, to increase the pressure of a draw product stream before the draw product stream is transported across an osmotic membrane (e.g., after the draw product stream has been transported across the permeate side of an osmotic membrane, and before the draw product stream is transported across the retentate side of an osmotic membrane).
Some embodiments comprise recovering at least a portion of the energy released by the reduction of the pressure of the portion of the first draw product stream transported across the first side of the second osmotic membrane. In some such embodiments, at least a portion of the recovered energy is used to increase the pressure of the portion of the first draw product stream transported across the first side of the second osmotic membrane, before the portion of the first draw product stream is transported across the first side of the second osmotic membrane. For example, referring to FIG. 2B, in some embodiments, at least a portion of the energy released by reducing the pressure of second concentrated aqueous stream 226 (which includes the portion of first draw product stream 212 transported across first side 218 of second osmotic membrane 216) is recovered. In some such embodiments, at least a portion of the recovered energy is used to increase the pressure of at least a portion of first draw product stream 212 before it is transported across first side 218 of second osmotic membrane 216.
Some embodiments comprise recovering at least a portion of the energy released by the reduction of the pressure of the portion of the second draw product stream transported across the first side of the third osmotic membrane. In some such embodiments, at least a portion of the recovered energy is used to increase the pressure of the portion of the second draw product stream transported across the first side of the third osmotic membrane, before the portion of the second draw product stream is transported across the first side of the third osmotic membrane. For example, referring to FIG. 2B, in some embodiments, at least a portion of the energy released by reducing the pressure of third concentrated aqueous stream 238 (which includes the portion of second draw product stream 224 transported across first side 230 of third osmotic membrane 228) is recovered. In some such embodiments, at least a portion of the recovered energy is used to increase the pressure of at least a portion of second draw product stream 224 before it is transported across first side 230 of third osmotic membrane 228.
Some embodiments comprise recovering at least a portion of the energy released by the reduction of the pressure of the portion of the third draw product stream transported across the first side of the fourth osmotic membrane. In some such embodiments, at least a portion of the recovered energy is used to increase the pressure of the portion of the third draw product stream transported across the first side of the fourth osmotic membrane, before the portion of the third draw product stream is transported across the first side of the fourth osmotic membrane. For example, referring to FIG. 2B, in some embodiments, at least a portion of the energy released by reducing the pressure of fourth concentrated aqueous stream 250 (which includes the portion of third draw product stream 236 transported across first side 242 of fourth osmotic membrane 240) is recovered. In some such embodiments, at least a portion of the recovered energy is used to increase the pressure of at least a portion of third draw product stream 236 before it is transported across first side 242 of fourth osmotic membrane 240.
Certain embodiments comprise recovering at least a portion of the energy released by the reduction of the pressure of a stream that exits a retentate side of an upstream osmotic membrane, and at least a portion of the energy that is recovered can be used to increase the pressure of a stream that is transported across the retentate side of a downstream osmotic membrane (i.e., an osmotic membrane that is downstream of the upstream osmotic membrane). In some embodiments, at least a portion of the energy recovered via the reduction of the pressure of the stream that exits the retentate side of the upstream osmotic membrane can be used to increase the pressure of a stream that exits the permeate side of the upstream osmotic membrane. In some such embodiments, at least a portion of the stream that exits the permeate side of the upstream osmotic membrane can then be transferred across the retentate side of a downstream osmotic membrane.
Certain embodiments comprise recovering at least a portion of the energy released by reducing the pressure of the first concentrated aqueous stream that exits the first side of the first osmotic membrane. In some such embodiments, at least a portion of the recovered energy is used to increase the pressure of at least a portion of the first draw product stream before it is transported across the first side of the second osmotic membrane. At least a portion, or all, of the first draw product stream may originate, for example, from the permeate side of the first osmotic membrane. For example, referring to FIG. 2B, in some embodiments, at least a portion of the energy released by reducing the pressure of concentrated aqueous stream 214 is recovered. In some such embodiments, at least a portion of the recovered energy is used to increase the pressure of at least a portion of first draw product stream 212 (which originates from second side 206 (the permeate side) of first osmotic membrane 202) before it is transported across first side 218 of second osmotic membrane 216.
Some embodiments comprise recovering at least a portion of the energy released by reducing the pressure of the second concentrated aqueous stream that exits the first side of the second osmotic membrane. In some such embodiments, at least a portion of the recovered energy is used to increase the pressure of at least a portion of the second draw product stream before it is transported across the first side of the third osmotic membrane. At least a portion, or all, of the second draw product stream may originate, for example, from the permeate side of the second osmotic membrane. For example, referring to FIG. 2B, in some embodiments, at least a portion of the energy released by reducing the pressure of second concentrated aqueous stream 226 is recovered. In some such embodiments, at least a portion of the recovered energy is used to increase the pressure of at least a portion of second draw product stream 224 (which originates from second side 220 (the permeate side) of second osmotic membrane 216) before it is transported across first side 230 of third osmotic membrane 228.
Certain embodiments comprise recovering at least a portion of the energy released by reducing the pressure of the third concentrated aqueous stream that exits the first side of the third osmotic membrane. In some such embodiments, at least a portion of the recovered energy is used to increase the pressure of at least a portion of the third draw product stream before it is transported across the first side of the fourth osmotic membrane. At least a portion, or all, of the third draw product stream may originate, for example, from the permeate side of the third osmotic membrane. For example, referring to FIG. 2B, in some embodiments, at least a portion of the energy released by reducing the pressure of third concentrated aqueous stream 238 is recovered. In some such embodiments, at least a portion of the recovered energy is used to increase the pressure of at least a portion of third draw product stream 236 (which originates from second side 232 (which is the permeate side) of third osmotic membrane 228) before it is transported across first side 242 of fourth osmotic membrane 240.
According to certain embodiments, combinations of the energy recovery methods described above can be employed. For example, some embodiments comprise recovering at least a portion of the energy released by the reduction of the pressure of a stream that exits a retentate side of an upstream osmotic membrane and recovering at least a portion of energy released by the reduction of the pressure of a stream that exits a retentate side of a downstream osmotic membrane (i.e., an osmotic membrane that is downstream of the upstream osmotic membrane). In some such embodiments, at least a portion of the energy recovered from the reduction of the pressure of the stream that exits the retentate side of the upstream osmotic membrane and at least a portion of the energy recovered from the reduction of the pressure of the stream that exits the retentate side of the downstream osmotic membrane are used to increase the pressure of another stream in the system (e.g., to increase the pressure of the stream that exits the permeate side of the upstream osmotic membrane and/or to increase the pressure of the stream that enters the retentate side of the downstream osmotic membrane).
For example, referring to FIG. 2B, some embodiments comprise (1) recovering at least a portion of the energy released by the reduction of the pressure of concentrated aqueous stream 238 which exits first side 230 (which is the retentate side) of third osmotic membrane 228 (which is upstream of fourth osmotic membrane 240) and (2) recovering at least a portion of energy released by the reduction of the pressure of concentrated aqueous stream 250 which exits first side 242 (which is the retentate side) of osmotic membrane 240 (which is downstream of third osmotic membrane 228). In some such embodiments, at least a portion of the energy recovered from the reduction of the pressure of concentrated aqueous stream 238 and at least a portion of the energy recovered from the reduction of the pressure of concentrated aqueous stream 250 are used to increase the pressure of third draw product stream 236, which exits second side 228 of third osmotic membrane and/or to increase the pressure of the portion of third draw product stream 236 that is transported across first side 242 of fourth osmotic membrane 240 before the portion of third draw product stream 236 is transported across first side 242 of fourth osmotic membrane 240. In some such embodiments, a first pressure exchange device can be used to transfer energy from stream 238 to stream 236, and a second pressure exchange device can be used to transfer energy from stream 250 to stream 236.
As another example, again referring to FIG. 2B, in some embodiments, fourth osmotic membrane 240 is not present (as it is an optional feature). Some embodiments comprise (1) recovering at least a portion of the energy released by the reduction of the pressure of concentrated aqueous stream 226 which exits first side 218 (which is the retentate side) of second osmotic membrane 216 (which is upstream of third osmotic membrane 228) and (2) recovering at least a portion of energy released by the reduction of the pressure of concentrated aqueous stream 238 which exits first side 230 (which is the retentate side) of third osmotic membrane 228 (which is downstream of second osmotic membrane 216). In some such embodiments, at least a portion of the energy recovered from the reduction of the pressure of concentrated aqueous stream 226 and at least a portion of the energy recovered from the reduction of the pressure of concentrated aqueous stream 238 are used to increase the pressure of second draw product stream 224, which exits second side 220 of second osmotic membrane 216 and/or to increase the pressure of the portion of second draw product stream 224 that is transported across first side 218 of third osmotic membrane 228 before the portion of second draw product stream 224 is transported across first side 230 of third osmotic membrane 228. In some such embodiments, a first pressure exchange device can be used to transfer energy from stream 226 to stream 224, and a second pressure exchange device can be used to transfer energy from stream 238 to stream 224.
According to certain embodiments, the recovery of energy from multiple streams (e.g., from a stream that exits a retentate side of an upstream osmotic membrane and from a stream that exits a retentate side of a downstream osmotic membrane), as described in the preceding paragraphs, can be used to pressurize a stream that is transported to the retentate side of the final osmotic membrane in a series of osmotic membranes. The “final” osmotic membrane, in this context, refers to the osmotic membrane that produces the final aqueous product, and after which, no additional osmosis steps are performed. Referring to FIG. 2B, for example, in some embodiments in which fourth osmotic membrane 240 is present, fourth osmotic membrane 240 can be the final osmotic membrane in a series of osmotic membranes. In some such embodiments, third osmotic membrane may be the penultimate osmotic membrane in a series of osmotic membranes. In some such embodiments, one or more intermediate osmotic membranes can be positioned between second osmotic membrane 216 and third osmotic membrane 228 within the series of osmotic membranes. In certain such embodiments, energy is recovered by reducing the pressure of concentrated aqueous stream 238 and by reducing the pressure of concentrated aqueous stream 250, and at least portions of the energies recovered from the reduction of the pressure of concentrated aqueous stream 238 and concentrated aqueous stream 250 are used to increase the pressure of third draw product stream 236 (e.g., as it exits second side 232 of third osmotic membrane 228 and/or before it is fed to first side 242 of fourth osmotic membrane 240). In some embodiments, fourth draw product stream 248 forms all or part of a final product stream (e.g., purified water), and, in some such cases, no further osmosis steps are performed on stream 248.
As another example, again referring to FIG. 2B, in some embodiments, fourth osmotic membrane is absent. In some embodiments, third osmotic membrane 228 can be the final osmotic membrane in a series of osmotic membranes. In some such embodiments, second osmotic membrane 216 may be the penultimate osmotic membrane in a series of osmotic membranes. In certain such embodiments, energy is recovered by reducing the pressure of concentrated aqueous stream 226 and by reducing the pressure of concentrated aqueous stream 238, and at least portions of the energies recovered from the reduction of the pressure of concentrated aqueous stream 226 and concentrated aqueous stream 238 are used to increase the pressure of second draw product stream 224 (e.g., as it exits second side 220 of second osmotic membrane 216 and/or before it is fed to first side 230 of third osmotic membrane 228). In some embodiments, third draw product stream 236 forms all or part of a final product stream (e.g., purified water), and, in some such cases, no further osmosis steps are performed on stream 236.
Energy from a pressurized stream can be recovered via any suitable method. For example, in some embodiments, a pressure exchange device can be used to recover energy from a pressurized stream. Those of ordinary skill in the art are familiar with pressure exchange devices, in which pressure energy from a high pressure fluid stream is transferred to a low pressure fluid stream. An exemplary type of pressure exchange device is a rotary pressure exchanger, for example, as described in U.S. Pat. No. 7,306,437. For example, in some embodiments, energy (e.g., as direct hydraulic pressure) can be recovered by directly contacting a pressurized stream with a stream at a lower pressure, such that the lower pressure stream is pressurized and the higher pressure stream is depressurized (e.g., throttled). Energy can also be recovered in the system using other devices such as, for example, a turbine (e.g., a Pelton wheel).
The systems and methods described herein can be used to process a variety of aqueous feed streams. According to certain embodiments, the stream fed to the desalination system is an aqueous stream comprising at least one solubilized ion species. For example, referring to FIGS. 2A-2B, aqueous feed stream 208 can comprise an aqueous stream comprising at least one solubilized ion species. The solubilized ion(s) may originate, for example, from a salt that has been dissolved in the aqueous stream. A solubilized ion is generally an ion that has been solubilized to such an extent that the ion is no longer ionically bonded to a counter-ion. The aqueous feed stream can comprise any of a number of solubilized ion species including, but not limited to, Na+, Mg2+, Ca2+, Sr2+, Ba2+, Cl, carbonate anions, bicarbonate anions, sulfate anions, bisulfate anions, and/or dissolved silica. In some embodiments, the aqueous feed stream comprises at least one solubilized monovalent cation (i.e., a cation with a redox state of +1 when solubilized). For example, in some embodiments, the aqueous feed stream comprises Na+ and/or K+. In certain embodiments, the aqueous feed stream comprises at least one monovalent anion (i.e., an anion having redox state of −1 when solubilized). For example, in some embodiments, the aqueous feed stream comprises Cl and/or Br. In some embodiments, the aqueous feed stream comprises at least one monovalent cation and at least one monovalent anion. In some embodiments, the aqueous feed stream comprises one or more divalent cations (i.e., a cation with a redox state of +2 when solubilized) and/or one or more divalent anions (i.e., an anion with a redox state of −2 when solubilized). Cations and/or anions having other valencies may also be present in the aqueous feed stream, in some embodiments.
In some embodiments, the total concentration of solubilized ions in the aqueous feed stream fed to the first osmotic membrane (e.g., stream 208 fed to first osmotic membrane 202 in FIGS. 2A-2B) can be relatively high. As noted elsewhere, one advantage associated with certain embodiments is that initial aqueous feed streams with relatively high solubilized ion concentrations can be desalinated without the use of energy intensive desalination methods. In certain embodiments, the total concentration of solubilized ions in the aqueous feed stream transported to the first osmotic membrane is at least about 60,000 ppm, at least about 80,000 ppm, or at least about 100,000 ppm (and/or, in some embodiments, up to about 500,000 ppm, or more). Aqueous feed streams with solubilized ion concentrations outside these ranges could also be used.
According to certain embodiments, the aqueous feed stream that is transported to the first osmotic membrane (e.g., stream 208 fed to first osmotic membrane 202 in FIGS. 2A-2B) comprises a suspended and/or emulsified immiscible phase. Generally, a suspended and/or emulsified immiscible phase is a material that is not soluble in water to a level of more than 10% by weight at the temperature and other conditions at which the stream is operated. In some embodiments, the suspended and/or emulsified immiscible phase comprises oil and/or grease. The term “oil” generally refers to a fluid that is more hydrophobic than water and is not miscible or soluble in water, as is known in the art. Thus, the oil may be a hydrocarbon in some embodiments, but in other embodiments, the oil may comprise other hydrophobic fluids. In some embodiments, at least about 0.1 wt %, at least about 1 wt %, at least about 2 wt %, at least about 5 wt %, or at least about 10 wt % (and/or, in some embodiments, up to about 20 wt %, up to about 30 wt %, up to about 40 wt %, up to about 50 wt %, or more) of the aqueous feed stream is made up of a suspended and/or emulsified immiscible phase.
In certain embodiments, the first osmotic membrane is configured such that little or none of the suspended and/or emulsified immiscible phase is transported through the first osmotic membrane. For example, in some embodiments, less than about 10 wt %, less than about 5 wt %, less than about 2 wt %, less than about 1 wt %, or substantially none of the suspended and/or emulsified immiscible phase is transported through the first osmotic membrane as the aqueous feed stream is transported across the first osmotic membrane.
While the first osmotic membrane can be used to separate a suspended and/or emulsified immiscible phase from an incoming aqueous feed stream, such separation is optional. For example, in some embodiments, the aqueous feed stream transported to the desalination system is substantially free of a suspended and/or emulsified immiscible phase. In certain embodiments, one or more separation units upstream of the first osmotic membrane can be used to at least partially remove a suspended and/or emulsified immiscible phase from an aqueous feed stream before the aqueous feed stream is transported to the first osmotic membrane. Non-limiting examples of such systems are described, for example, in International Patent Publication No. WO 2015/021062, published on Feb. 12, 2015, which is incorporated herein by reference in its entirety for all purposes.
In some embodiments, the aqueous feed stream can be derived from seawater, ground water, brackish water, and/or the effluent of a chemical process. In the oil and gas industry, for example, one type of aqueous feed stream that may be encountered is produced water (e.g., water that emerges from oil or gas wells along with the oil or gas). Due to the length of time produced water has spent in the ground, and due to high subterranean pressures and temperatures that may increase the solubility of certain salts and minerals, produced water often comprises relatively high concentrations of dissolved salts and minerals. For example, some produced water streams may comprise a supersaturated solution of dissolved strontium sulfate (SrSO4). In contrast, another type of aqueous feed stream that may be encountered in the oil and gas industry is flowback water (e.g., water that is injected as a fracking fluid during hydraulic fracturing operations and subsequently recovered). Flowback water often comprises a variety of constituents used in fracking, including surfactants, proppants, and viscosity reducing agents, but often has a lower salinity than produced water. In some cases, the systems and methods described herein can be used to at least partially desalinate aqueous feed streams derived from such process streams.
The first draw inlet stream (e.g., stream 210 in FIGS. 2A-2B) can comprise, according to certain embodiments, any component(s) suitable for imparting an appropriate osmotic pressure to perform the functions described herein. In some embodiments, the first draw inlet stream is an aqueous solution comprising one or more solubilized species, such as one or more dissolved ions and/or one or more dissociated molecules. For example, in some embodiments, the first draw inlet stream comprises Na+, Mg2+, Ca2+, Sr2+, Ba2+, and/or Cl. In some embodiments, the first draw inlet stream comprises at least one solubilized monovalent cation, such as Na+ and/or K+. In certain embodiments, the first draw inlet stream comprises at least one monovalent anion, such as Cl and/or Br. Cations and/or anions having other valencies may also be present in the first draw inlet stream. Other species could also be used in the draw stream. For example, in some embodiments, the first draw inlet stream can be an aqueous stream comprising a solubilized non-ionic species, such as ammonia (NH3).
The second draw inlet stream (e.g., stream 222 in FIGS. 2A-2B) can also comprise any component(s) suitable for imparting an appropriate osmotic pressure to perform the functions described herein, according to certain embodiments. In some embodiments, the second draw inlet stream is an aqueous solution comprising one or more solubilized species, such as one or more dissolved ions and/or one or more dissociated molecules. For example, in some embodiments, the second draw inlet stream comprises Na+, Mg2+, Ca2+, Sr2+, Ba2+, and/or Cl. In some embodiments, the second draw inlet stream comprises at least one solubilized monovalent cation, such as Na+ and/or K+. In certain embodiments, the second draw inlet stream comprises at least one monovalent anion, such as Cl and/or Br. Cations and/or anions having other valencies may also be present in the second draw inlet stream. Other species could also be used in the second draw inlet stream. For example, in some embodiments, the second draw inlet stream can be an aqueous stream comprising a solubilized non-ionic species, such as ammonia (NH3). The second draw inlet stream can included solubilized species (e.g., solubilized ion species) that are the same as or different from those present in the first draw inlet stream. In some embodiments, the total molar concentration (in units of molarity) of solubilized species (e.g., solubilized ions) in the second draw inlet stream is lower than the total molar concentration of solubilized species (e.g., solubilized ions) in the first draw inlet stream.
The third draw inlet stream (e.g., stream 234 in FIG. 2B) can also, according to certain embodiments, comprise any component(s) suitable for imparting an appropriate osmotic pressure to perform the functions described herein. In some embodiments, the third draw inlet stream is an aqueous solution comprising one or more solubilized species, such as one or more ions and/or one or more dissociated molecules. For example, in some embodiments, the third draw inlet stream comprises Na+, Mg2+, Ca2+, Sr2+, Ba2+, and/or Cl. In some embodiments, the third draw inlet stream comprises at least one solubilized monovalent cation, such as Na+ and/or K+. In certain embodiments, the third draw inlet stream comprises at least one monovalent anion, such as Cl and/or Br. Cations and/or anions having other valencies may also be present in the third draw inlet stream. Other species could also be used in the third draw inlet stream. For example, in some embodiments, the third draw inlet stream can be an aqueous stream comprising a solubilized a non-ionic species, such as ammonia (NH3). The third draw inlet stream can included solubilized species (e.g., solubilized ions) that are the same as or different from those present in the first and/or second draw inlet stream. In some embodiments, the total molar concentration of solubilized species (e.g., solubilized ions) in the third draw inlet stream is lower than the total molar concentration of solubilized species (e.g., solubilized) ions in the second draw inlet stream.
The fourth draw inlet stream (e.g., stream 246 in FIG. 2B) can also comprise any component(s) suitable for imparting an appropriate osmotic pressure to perform the functions described herein, according to certain embodiments. In some embodiments, the fourth draw inlet stream is an aqueous solution comprising one or more solubilized species, such as one or more dissolved ions and/or one or more dissociated molecules. For example, in some embodiments, the fourth draw inlet stream comprises Na+, Mg2+, Ca2+, Sr2+, Ba2+, and/or Cl. In some embodiments, the fourth draw inlet stream comprises at least one solubilized monovalent cation, such as Na+ and/or K+. In certain embodiments, the fourth draw inlet stream comprises at least one monovalent anion, such as Cl and/or Br. Cations and/or anions having other valencies may also be present in the fourth draw inlet stream. Other species could also be used in the fourth draw inlet stream. For example, in some embodiments, the fourth draw inlet stream is an aqueous stream comprising a solubilized non-ionic species, such as ammonia (NH3). The fourth draw inlet stream can include solubilized ion species that are the same as or different from those present in the first, second, and/or third draw inlet streams. In some embodiments, the total molar concentration of solubilized species (e.g., solubilized ions) in the fourth draw inlet stream is lower than the total molar concentration of solubilized species (e.g., solubilized ions) in the third draw inlet stream.
Those of ordinary skill in the art, given the insight provided by the present disclosure, would be capable of selecting appropriate components for use in the various draw streams described herein.
The draw inlet streams may be prepared, according to certain embodiments, by suspending and/or dissolving one or more species in a solvent, such as an aqueous solvent) to solubilize the species in the solvent. For example, in some embodiments, one or more draw inlet streams can be made by dissolving one or more solid salts in an aqueous solvent. Non-limiting examples of salts that may be dissolved in water include NaCl, CaCl2, MgCl2, and the like. In some embodiments, the draw stream can be prepared by mixing ammonia with water. In certain embodiments, the draw stream can be prepared by dissolving one or more ammonia salts (e.g., ammonium bicarbonate, ammonium carbonate, and/or ammonium carbamate) in water. In some embodiments, the draw stream can be prepared by dissolving ammonia and carbon dioxide gasses in water.
Those of ordinary skill in the art are familiar with osmotic membranes. The membrane medium can comprise, for example, a metal, a ceramic, a polymer (e.g., polyamides, polyethylenes, polyesters, poly(tetrafluoroethylene), polysulfones, polycarbonates, polypropylenes, poly(acrylates)), and/or composites or other combinations of these. Osmotic membranes generally allow for the selective transport of water through the membrane, in which water is capable of being transmitted through the membrane while solubilized species (e.g., ions) are inhibited from being transported through the membrane. Examples of commercially available osmotic membranes that can be used in association with certain of the embodiments described herein include, but are not limited to, those commercially available from Dow Water and Process Solutions (e.g., FilmTec™ membranes), Hydranautics, GE Osmonics, and Toray Membrane, among others known to those of ordinary skill in the art.
It should be understood that, where a single membrane is shown or described, such single membranes could be replaced with multiple, parallel-connected osmotic membranes. The use of multiple, parallel-connected osmotic membranes can, for example, increase the capacity of the system.
U.S. Provisional Patent Application Ser. No. 62/198,413, filed Jul. 29, 2015, and entitled “Osmotic Desalination Methods and Associated Systems” is incorporated herein by reference in its entirety for all purposes.
The following examples are intended to illustrate certain embodiments of the present invention, but do not exemplify the full scope of the invention.
Example 1
In this example, a single stage osmotic membrane system is described, which is used to perform draw-assisted reverse osmosis. The system contained a single nonporous membrane with a feed side, across which a pressurized influent feed stream flowed, and a draw side, across which an influent draw stream flowed.
The systems was operated as follows, with reference to the exemplary diagram shown in FIG. 1A. The system comprised an osmotic membrane 102 with a first side 104 and a second side 106. An influent aqueous feed stream 108 was transported across the first side 104, and an influent draw stream 110 was transported across the second side 106. Water was transported between the first side 104 and second side 106 of the osmotic membrane 102 to produce an aqueous stream 114, from the influent aqueous feed stream 108, and a draw product stream 112, from the draw stream 110.
The osmotic membrane 102 in this system was manufactured by Porifera, and had a total area of 1 m2 comprising a nonporous active layer on the first side 104 and a porous nonwoven structural support layer on the second side 106. The osmotic membrane was contained inside a counter-current plate and frame module, also manufactured by Porifera. Aqueous feed stream 108 and draw stream 110 were prepared by dissolving Sonoma sea salt in deionized water.
Aqueous feed stream 108 was pumped from a first vessel across the first side 104 of osmotic membrane 102 by a first diaphragm pump. The hydraulic pressure on the first side 104 was controlled by a Swagelok backpressure regulator at the outlet of the membrane module through which effluent aqueous stream 114 flowed. The aqueous stream 114 was collected in a second vessel. Draw stream 110 was pumped from a third vessel across the second side of osmotic membrane 102 by a second diaphragm pump. The effluent draw product stream 112 was collected in a fourth vessel.
Pressure was measured by dial indicators at the osmotic membrane module outlet through which the effluent aqueous stream 114 flowed and at the osmotic membrane module outlet through which the effluent draw product stream 112 flowed.
Transmembrane pressure was calculated as the difference between the pressure measured at these locations. Flow rates of the influent aqueous feed stream 108, of the effluent aqueous stream 114, of the influent draw stream 110, and of the effluent draw product stream 112 were measured gravimetrically by weighing the first, second, third and fourth vessel respectively at intervals of 10-15 minutes. The weight changes and interval between the weighings of each vessel were used to calculate the mass flow rate of each stream. Difference between the mass flow rate of aqueous feed stream 108 and aqueous stream 114, and the difference between the mass flow rate of draw stream 110 and draw product stream 112 were averaged to calculate the flux across the osmotic membrane 102. Sodium concentration of each stream was analyzed using an inductively coupled plasma optical emission spectrometer manufactured by Perkin Elmer from samples collected from each of the four vessels at increments of 10-15 minutes.
The salinity of the draw stream source was varied and the effect of the variation on transmembrane flux was measured. The osmotic membrane system was allowed to reach a steady state by operating for one hour at fixed conditions before flow rate, pressure, and salinity measurements were taken. A source of aqueous feed stream 108 was prepared and measured to contain 1900 mg/L sodium. The transmembrane pressure was adjusted to 17 psi. The flow rate of the aqueous feed stream 108 was 45.77 ml/min, and the flow rate of the draw stream 110 was 39.28. The salinity of the draw stream source and the resulting transmembrane flux is shown in Table 1.
TABLE 1
Trial 1 2 3
Draw stream sodium concentration 0.000 851.0 1594
[mg/L]
Transmembrane flux [ml/min] −5.971 1.301 5.535
In Table 1, the flux is shown to reverse direction between trials 1 and 2, and increase further in trial 3. In trial 1, the transmembrane pressure was not sufficient to overcome the osmotic pressure difference across the membrane 102, so water flowed across the osmotic membrane 102 from the second side 106 to the first side 104. In trial 2, the salinity of the draw stream 110 reduced the osmotic pressure difference between the two sides. Although the salinity of the feed stream 108 was greater than the salinity of the draw stream 110, the resulting osmotic pressure difference was not sufficient to overcome the transmembrane pressure, resulting in a positive flux from the first side 104 to the second side 106. In trial 3, the osmotic pressure difference is further reduced by the increased salinity of the draw stream 110, resulting in a greater positive flux.
Example 2
In this example, a multistaged osmotic membrane cascade was simulated by repeated experiments on a single osmotic membrane system in which the draw stream product from previous trials was used as the feed stream for each trial after the first.
The systems was operated as follows, with reference to the exemplary diagram shown in FIG. 1A. The system comprised an osmotic membrane 102 with a first side 104 and a second side 106. An influent aqueous feed stream 108 was transported across the first side 104, and an influent draw stream 110 was transported across the second side 106. Water was transported between the first side 104 and second side 106 of the osmotic membrane 102 to produce an aqueous stream 114, from the influent aqueous feed stream 108, and a draw product stream 112, from the draw stream 110.
The osmotic membrane 102 in this system was manufactured by Porifera, and had a total area of 1 m2 comprising a nonporous active layer on the first side 104 and a porous nonwoven structural support layer on the second side 106. The osmotic membrane was contained inside a counter-current plate and frame module, also manufactured by Porifera. Aqueous feed stream 108 and draw stream 110 were prepared by dissolving Sonoma sea salt in deionized water.
Aqueous feed stream 108 was pumped from a first vessel across the first side 104 of osmotic membrane 102 by a first diaphragm pump. The hydraulic pressure on the first side 104 was controlled by a Swagelok backpressure regulator at the outlet of the membrane module through which effluent aqueous stream 114 flowed. The aqueous stream 114 was collected in a second vessel. Draw stream 110 was pumped from a third vessel across the second side of osmotic membrane 102 by a second diaphragm pump. The effluent draw product stream 112 was collected in a fourth vessel.
Pressure was measured by dial indicators at the osmotic membrane module outlet through which the effluent aqueous stream 114 flowed and at the osmotic membrane module outlet through which the effluent draw product stream 112 flowed.
Transmembrane pressure was calculated as the difference between the pressure measured at these locations. Flow rates of the influent aqueous feed stream 108, of the effluent aqueous stream 114, of the influent draw stream 110, and of the effluent draw product stream 112 were measured gravimetrically by weighing the first, second, third and fourth vessel respectively at intervals of 10-15 minutes. The weight changes and interval between the weighings of each vessel were used to calculate the mass flow rate of each stream. The difference between the mass flow rate of aqueous feed stream 108 and aqueous stream 114, and the difference between the mass flow rate of draw stream 110 and draw product stream 112 were averaged to calculate the flux across the osmotic membrane 102. The sodium concentration of each stream was analyzed using an inductively coupled plasma optical emission spectrometer manufactured by Perkin Elmer from samples collected from each of the four vessels at increments of 10-15 minutes.
The salinity of the aqueous feed stream 108 and the draw stream 110 were varied in successive trials to simulate a membrane cascade. In the first trial, a starting aqueous feed stream salinity and draw stream salinity was selected. The resulting draw stream product of the first trial was collected and used as the source of the aqueous feed stream 108 in the second trial. The resulting draw product stream of the second trial was collected and used as the source of the aqueous feed stream 108 in the third trial. The resulting draw product stream of the third trial was collected and used as the source of the aqueous feed stream 108 in the fourth trial. The trials, considered together, simulate the system configuration described by FIG. 2B in which a first draw product stream 212, flowing from a first osmotic membrane 202, is fed to the first side of a second osmotic membrane 216. Downstream membranes are similarly fed feed streams comprising the draw product stream resulting from upstream membranes. The cascade experiment was performed for first trial feed streams of 5000 ppm and 50,000 ppm. A set of single stage trials were also performed for each first trial feed salinity, in which the draw stream salinity was equal to the final draw stream salinity of the corresponding cascade experiment. The results of the 5000 ppm feed stream cascade experiment and corresponding single-stage comparison experiment are displayed in Table 2. The results of the 50,000 ppm feed stream experiments are displayed in Table 3.
TABLE 2
Feed Salinity Draw Salinity Flux Pressure
Stage [mg/L] [mg/L] [ml/min] [psi]
1 50,000 49,000 2.4 ± 0.1 17
2 Draw stream product 48,000 2.12 ± 0.02 17
from stage 1
3 Draw stream product 47,000 1.98 ± 0.04 17
from stage 2
Single 50,000 47,000 1.3 17
stage
TABLE 3
Feed Salinity Draw Salinity Flux Pressure
Stage [mg/L] [mg/L] [ml/min] [psi]
1 5,000 4,000 4.63 ± 0.7 17
2 Draw stream product 3,000 5.58 ± 0.3 17
from stage 1
3 Draw stream product 2,000  6.4 ± 0.2 17
from stage 2
4 Draw stream product 1,000 7.78 ± 0.4 17
from stage 3
Single 5,000 1,000 −0.43 ± 0.07 17
stage
In Tables 2 and 3, the flux through each of the cascade stages is shown greater than the flux through the corresponding single stage trial. The greater flux through the cascade system indicates that a greater amount of fresh water may be recovered from a saline stream when a cascade configuration is used. In Table 3, the corresponding single stage trial is shown to have a negative flux, indicating an insufficient transmembrane pressure difference. These results demonstrate that a lower transmembrane pressure may be required to overcome an osmotic pressure gradient when a cascade configuration is used.
Prophetic Example 1
This prophetic example describes a desalination system in which an initial forward osmosis process is combined with a series of downstream reverse osmosis processes to produce an aqueous product stream with a higher purity of water than the initial aqueous feed stream.
An exemplary process is shown in the schematic diagram of FIG. 3A. In FIG. 3A, an aqueous feed stream including 10 wt % dissolved NaCl is transported to a first side of a first osmotic membrane. An aqueous draw solution comprising 22 wt % dissolved NaCl is transported to the second side of the first osmotic membrane, in a counter-flow arrangement relative to the aqueous feed stream. The first osmotic membrane is used to perform forward osmosis, such that a concentrated reject brine stream containing 20 wt % dissolved NaCl is produced and transported away from the first side of the first osmotic membrane, and a diluted draw solution containing 10.47 wt % dissolved NaCl is produced and transported away from the second side of the first osmotic membrane.
In FIG. 3A, the diluted draw solution from the first osmotic membrane is transported, using a pump, to the first side of a second osmotic membrane. An aqueous intermediate draw solution comprising 20 wt % dissolved NaCl is transported to the second side of the second osmotic membrane, in a counter-flow arrangement relative to the dilute draw solution stream. The counter-flow arrangement of the diluted draw solution from the first osmotic membrane and the aqueous intermediate draw solution—and the selection of appropriate concentrations and flow rates—can allow one to operate the second osmotic membrane such that the difference in osmotic pressures between the solutions on either side of the membrane relatively consistent across the facial area of the membrane. A hydraulic pressure of 20 bar is applied to the first side of the second osmotic membrane, and a reverse osmosis process is performed such that a concentrated draw solution stream containing 22 wt % dissolved NaCl is produced and transported away from the first side of the second osmotic membrane, and a diluted intermediate draw solution containing 8.72 wt % dissolved NaCl is produced and transported away from the second side of the second osmotic membrane. At least a portion (or all) of the recovered concentrated draw solution stream can be throttled to a desired pressure (e.g., decreasing the pressure by about 14 bar to a pressure of about 6 bar) and sent back to the first osmotic membrane in a closed or at least partially closed loop.
In FIG. 3A, the diluted intermediate draw solution from the second osmotic membrane is transported, using a pump, to the first side of a third osmotic membrane. An aqueous draw solution comprising 18 wt % dissolved NaCl is transported to the second side of the third osmotic membrane, in a counter-flow arrangement relative to the dilute intermediate draw solution stream. A hydraulic pressure of 20 bar is applied to the first side of the third osmotic membrane, and a reverse osmosis process is performed such that a concentrated draw solution stream containing 20 wt % dissolved NaCl is produced and transported away from the first side of the third osmotic membrane, and a diluted intermediate draw solution containing 6.98 wt % dissolved NaCl is produced and transported away from the second side of the third osmotic membrane. At least a portion (or all) of the recovered concentrated draw solution stream can be throttled to a desired pressure (e.g., decreasing the pressure by about 14 bar to a pressure of about 6 bar) and sent back to the second osmotic membrane in a closed or at least partially closed loop.
Third, fourth, and fifth reverse osmosis processes (not illustrated in FIG. 3A) are also performed, such that a further diluted aqueous stream containing 1.83 wt % dissolved NaCl is produced. The diluted aqueous stream containing 1.83 wt % dissolved NaCl is transported to the first side of a seventh osmotic membrane (to perform a sixth reverse osmosis process). An additional draw solution containing 10 wt % of dissolved NaCl is transported to the second side of the seventh osmotic membrane. A hydraulic pressure of 20 bar is applied to the first side of the seventh osmotic membrane, and a reverse osmosis process is performed such that a concentrated aqueous stream containing 12 wt % dissolved NaCl is produced and transported away from the first side of the seventh osmotic membrane, and a final product stream containing substantially pure water (about 0.15% NaCl) is produced and transported away from the second side of the seventh osmotic membrane. At least a portion (or all) of the recovered concentrated draw solution stream can be throttled to a desired pressure (e.g., decreasing the pressure by about 14 bar to a pressure of about 6 bar) and sent back to the sixth osmotic membrane in a closed or at least partially closed loop.
Prophetic Example 2
This prophetic example describes the use of energy recovery in a desalination system in which an initial forward osmosis process is combined with a series of downstream reverse osmosis processes to produce an aqueous product stream with a higher purity of water than the initial aqueous feed stream.
FIG. 3B is a schematic illustration of an exemplary desalination system in which energy is recovered at multiple points in the system. The energy can be recovered as direct hydraulic pressure, for example, using a pressure exchange device (instead of or in addition to a throttle). The process illustrated in FIG. 3B includes that same four initial osmotic stages as described above with respect to FIG. 3A (with similar streams and component concentrations, and similar osmotic membranes), except energy recovery devices have been added to the embodiment shown in FIG. 3B.
In FIG. 3B, the 22 wt % dissolved NaCl recovered draw solution from the second osmotic membrane (which is at a higher hydraulic pressure than the dilute 10.47 wt % dissolved NaCl draw solution exiting the first osmotic membrane) can be used to transfer energy (in the form of pressure) via direct contact (e.g., in a rotary pressure exchange device) with the dilute 10.47 wt % dissolved NaCl draw solution before the dilute draw solution is pressurized and sent to the second osmotic membrane. During this process, the 22 wt % dissolved NaCl recovered draw solution is depressurized (throttled). While a rotary pressure exchange device is illustrated in FIG. 3B, other devices (e.g., a Pelton wheel) could also be used.
Also in FIG. 3B, the 20 wt % dissolved NaCl recovered draw solution (which is at a higher hydraulic pressure than the 8.72 wt % dissolved NaCl dilute draw solution) can be used to transfer energy (in the form of pressure) via direct contact (e.g., in a rotary pressure exchange device) with the dilute 8.72 wt % dissolved NaCl draw solution before the dilute draw solution is pressurized and sent to the third osmotic membrane. During this process, the 20 wt % dissolved NaCl recovered draw solution is depressurized (throttled).
Also in FIG. 3B, the 18 wt % dissolved NaCl recovered draw solution (which is at a higher hydraulic pressure than the 6.98 wt % dissolved NaCl dilute draw solution) can be used to transfer energy (in the form of pressure) via direct contact (e.g., in a rotary pressure exchange device) with the dilute 6.98 wt % dissolved NaCl draw solution before the dilute draw solution is pressurized and sent to the fourth osmotic membrane. During this process, the 18 wt % dissolved NaCl recovered draw solution is depressurized (throttled).
Prophetic Example 3
This prophetic example describes the operation of an osmotic membrane separator in which flow rates, osmotic pressures, and hydraulic pressures of inlet streams are selected to balance the net osmotic driving force across the facial area of the osmotic membrane.
A schematic illustration of the osmotic membrane separator is shown in FIG. 4A. The osmotic membrane separator comprises osmotic membrane 102, defining a first side 104 and a second side 106. Feed stream 108 has a mass flow rate mF,i, an osmotic pressure πF,i, and a hydraulic pressure PF. Concentrated aqueous stream 114 has a mass flow rate mF,o, an osmotic pressure πF,o, and a hydraulic pressure PF. Draw inlet stream 110 has a mass flow rate mD,i, an osmotic pressure πD,i, and a hydraulic pressure PD. Draw product stream 112 has a mass flow rate mD,o, an osmotic pressure πD,o, and a hydraulic pressure PD. Feed stream 108 is transported across first side 104 of osmotic membrane 102, and draw inlet stream 110 is transported across second side 106 of osmotic membrane 102 in a direction opposite the direction of feed stream 108. In this way, the osmotic separator is operated in a counterflow configuration. Positions along membrane 102 can be denoted along the x-axis illustrated in FIG. 4A, with x=0 corresponding to a position closest to the aqueous inlet feed and draw product streams, and x=1 corresponding to the draw inlet and the concentrated aqueous stream outlet.
In one exemplary mode of operation, the aqueous feed stream 108 enters one side of the counterflow reverse osmosis membrane at position x=0, with a salt concentration of 100,000 ppm, a hydraulic pressure of 300 psi, and an osmotic pressure of 1311 psi. Draw inlet stream 110 can be a saline draw stream, entering the separator at the opposite side (i.e., at position x=1) with a salinity of 95,000 ppm, a hydraulic pressure of substantially 0, and an osmotic pressure of 1271 psi. The mass flow rate ratio of streams 108 and 110 is selected according to Equation 4, with C=1.
As aqueous feed stream 108 travels across membrane 102, some portion of the water within stream 108 passes through membrane 102 from first side 104 to second side 106. Because salts and/or other contaminants are excluded by membrane 102, the permeate is almost entirely pure water. Salt remains in the liquid on side 104 of membrane 102, so the concentration increases. When stream 114 exits the membrane separator (at position x=1), the osmotic pressure is 1531 psi.
As draw inlet stream 110 travels across side 106 of membrane 102 (in a direction opposite the direction of stream 108), it is diluted by the pure water permeating through membrane 102 (from side 104 to side 106). The mass flow of the salt remains unchanged, so salinity of the liquid on side 106 of membrane 102 drops, decreasing the osmotic pressure. When draw product stream 112 exits the membrane separator (at position x=0), the osmotic pressure is 1074 psi. In this example, the pressure drop across the membrane is assumed to be substantially 0. Thus, the net driving force scales linearly with salt concentration.
Because the mass flow rate ratios were balanced according to Equation 4, the change in net driving force across the membrane is minimized. FIG. 4B is a plot of osmotic pressure as a function of position across the osmotic membrane. As seen in FIG. 4B, the difference between the feed osmotic pressure and the draw osmotic pressure remains relatively constant across the osmotic membrane. In this example, the maximum net driving force and the minimum net driving force are within 9.05% of each other.
While several embodiments of the present invention have been described and illustrated herein, those of ordinary skill in the art will readily envision a variety of other means and/or structures for performing the functions and/or obtaining the results and/or one or more of the advantages described herein, and each of such variations and/or modifications is deemed to be within the scope of the present invention. More generally, those skilled in the art will readily appreciate that all parameters, dimensions, materials, and configurations described herein are meant to be exemplary and that the actual parameters, dimensions, materials, and/or configurations will depend upon the specific application or applications for which the teachings of the present invention is/are used. Those skilled in the art will recognize, or be able to ascertain using no more than routine experimentation, many equivalents to the specific embodiments of the invention described herein. It is, therefore, to be understood that the foregoing embodiments are presented by way of example only and that, within the scope of the appended claims and equivalents thereto, the invention may be practiced otherwise than as specifically described and claimed. The present invention is directed to each individual feature, system, article, material, and/or method described herein. In addition, any combination of two or more such features, systems, articles, materials, and/or methods, if such features, systems, articles, materials, and/or methods are not mutually inconsistent, is included within the scope of the present invention.
The indefinite articles “a” and “an,” as used herein in the specification and in the claims, unless clearly indicated to the contrary, should be understood to mean “at least one.”
The phrase “and/or,” as used herein in the specification and in the claims, should be understood to mean “either or both” of the elements so conjoined, i.e., elements that are conjunctively present in some cases and disjunctively present in other cases. Other elements may optionally be present other than the elements specifically identified by the “and/or” clause, whether related or unrelated to those elements specifically identified unless clearly indicated to the contrary. Thus, as a non-limiting example, a reference to “A and/or B,” when used in conjunction with open-ended language such as “comprising” can refer, in one embodiment, to A without B (optionally including elements other than B); in another embodiment, to B without A (optionally including elements other than A); in yet another embodiment, to both A and B (optionally including other elements); etc.
As used herein in the specification and in the claims, “or” should be understood to have the same meaning as “and/or” as defined above. For example, when separating items in a list, “or” or “and/or” shall be interpreted as being inclusive, i.e., the inclusion of at least one, but also including more than one, of a number or list of elements, and, optionally, additional unlisted items. Only terms clearly indicated to the contrary, such as “only one of” or “exactly one of,” or, when used in the claims, “consisting of,” will refer to the inclusion of exactly one element of a number or list of elements. In general, the term “or” as used herein shall only be interpreted as indicating exclusive alternatives (i.e. “one or the other but not both”) when preceded by terms of exclusivity, such as “either,” “one of,” “only one of,” or “exactly one of.” “Consisting essentially of,” when used in the claims, shall have its ordinary meaning as used in the field of patent law.
As used herein in the specification and in the claims, the phrase “at least one,” in reference to a list of one or more elements, should be understood to mean at least one element selected from any one or more of the elements in the list of elements, but not necessarily including at least one of each and every element specifically listed within the list of elements and not excluding any combinations of elements in the list of elements. This definition also allows that elements may optionally be present other than the elements specifically identified within the list of elements to which the phrase “at least one” refers, whether related or unrelated to those elements specifically identified. Thus, as a non-limiting example, “at least one of A and B” (or, equivalently, “at least one of A or B,” or, equivalently “at least one of A and/or B”) can refer, in one embodiment, to at least one, optionally including more than one, A, with no B present (and optionally including elements other than B); in another embodiment, to at least one, optionally including more than one, B, with no A present (and optionally including elements other than A); in yet another embodiment, to at least one, optionally including more than one, A, and at least one, optionally including more than one, B (and optionally including other elements); etc.
In the claims, as well as in the specification above, all transitional phrases such as “comprising,” “including,” “carrying,” “having,” “containing,” “involving,” “holding,” and the like are to be understood to be open-ended, i.e., to mean including but not limited to. Only the transitional phrases “consisting of” and “consisting essentially of” shall be closed or semi-closed transitional phrases, respectively, as set forth in the United States Patent Office Manual of Patent Examining Procedures, Section 2111.03.

Claims (28)

What is claimed is:
1. A method, comprising:
transporting an aqueous feed stream across a first side of an osmotic membrane;
transporting a draw inlet stream across a second side of the osmotic membrane such that water is transported from the aqueous feed stream through the osmotic membrane to the draw inlet stream to produce a draw product stream having a lower osmotic pressure than the draw inlet stream and a concentrated aqueous stream having a higher osmotic pressure than the aqueous feed stream, wherein the aqueous feed stream enters the first side of the osmotic membrane at a first lateral location of the osmotic membrane, and the draw inlet stream enters the second side of the osmotic membrane at a second lateral location of the osmotic membrane that is different than the first lateral location; and
directing the transport of the aqueous feed stream across the osmotic membrane and/or the draw inlet stream across the osmotic membrane such that the transmembrane net driving force at the entrance of the aqueous feed stream to the osmotic membrane and the transmembrane net driving force at the entrance of the draw inlet stream to the osmotic membrane are within about 10% of each other.
2. The method of claim 1, wherein the concentrated aqueous stream has a higher concentration of solubilized ions than the aqueous feed stream.
3. The method of claim 1, wherein the draw inlet stream has a higher osmotic pressure than an osmotic pressure of the aqueous feed stream.
4. The method of claim 1, wherein the draw inlet stream has a lower osmotic pressure than an osmotic pressure of the aqueous feed stream.
5. The method of claim 1, wherein the concentration of solubilized ions within the aqueous feed stream is at least about 60,000 ppm.
6. The method of claim 1, wherein, over at least about 90% of a facial area of the osmotic membrane, a transmembrane net driving force across the osmotic membrane is uniform to within about 10%.
7. The method of claim 1, wherein, at at least one location on the osmotic membrane, a difference between an osmotic pressure on the first side of the osmotic membrane and an osmotic pressure on the second side of the osmotic membrane is less than about 45 bar.
8. The method of claim 1, wherein the aqueous feed stream and the draw inlet stream are transported across the osmotic membrane in a counter-current configuration.
9. The method of claim 1, wherein the aqueous feed stream contains a suspended and/or emulsified immiscible phase.
10. A method, comprising:
transporting an aqueous feed stream containing solubilized ions across a first side of a first osmotic membrane;
transporting a first draw inlet stream across a second side of the first osmotic membrane such that water is transported from the aqueous feed stream through the first osmotic membrane to the first draw inlet stream to produce a first draw product stream having a lower osmotic pressure than the first draw inlet stream and a concentrated aqueous stream having a higher osmotic pressure than the aqueous feed stream;
transporting at least a portion of the first draw product stream from the second side of the first osmotic membrane across a first side of a second osmotic membrane;
transporting a second draw inlet stream across a second side of the second osmotic membrane; and
applying a hydraulic pressure to the first side of the second osmotic membrane such that water is transported from the first draw product stream through the second osmotic membrane to the second draw inlet stream to produce a second draw product stream having a lower osmotic pressure than the second draw inlet stream and a second concentrated aqueous stream having a higher osmotic pressure than the first draw product stream;
wherein a difference between an osmotic pressure within the aqueous feed stream and an osmotic pressure of the first draw inlet stream and a difference between an osmotic pressure within the first draw product stream and an osmotic pressure of the second draw inlet stream are within about 20% of each other.
11. The method of claim 10, wherein the concentrated aqueous stream has a higher concentration of solubilized ions than the aqueous feed stream.
12. The method of claim 10, wherein the first draw inlet stream has a higher osmotic pressure than an osmotic pressure of the aqueous feed stream.
13. The method of claim 10, wherein the first draw inlet stream has a lower osmotic pressure than an osmotic pressure of the aqueous feed stream.
14. The method of claim 10, wherein the concentration of solubilized ions within the aqueous feed stream is at least about 60,000 ppm.
15. The method of claim 10, wherein, over at least about 90% of a facial area of the first osmotic membrane, a transmembrane net driving force across the first osmotic membrane is uniform to within about 10%.
16. The method of claim 10, wherein, over at least about 90% of a facial area of the second osmotic membrane, a transmembrane net driving force across the second osmotic membrane is uniform to within about 10%.
17. The method of claim 10, wherein, at at least one location on the first osmotic membrane, a difference between an osmotic pressure on the first side of the first osmotic membrane and an osmotic pressure on the second side of the first osmotic membrane is less than about 45 bar.
18. The method of claim 10, wherein the aqueous feed stream and the first draw inlet stream are transported across the first osmotic membrane in a counter-current configuration.
19. The method of claim 10, wherein the first draw product stream and the second draw inlet stream are transported across the second osmotic membrane in a counter-current configuration.
20. A method, comprising:
transporting an aqueous feed stream across a first side of an osmotic membrane;
transporting a draw inlet stream across a second side of the osmotic membrane such that water is transported from the aqueous feed stream through the osmotic membrane to the draw inlet stream to produce a draw product stream having a lower osmotic pressure than the draw inlet stream and a concentrated aqueous stream having a higher osmotic pressure than the aqueous feed stream; and
directing the transport of the aqueous feed stream across the osmotic membrane and/or the draw inlet stream across the osmotic membrane such that over at least about 90% of a facial area of the osmotic membrane, a transmembrane net driving force across the osmotic membrane is uniform to within about 10%.
21. The method of claim 20, wherein the aqueous feed stream contains a suspended and/or emulsified immiscible phase and solubilized ions at a concentration of at least 60,000 ppm.
22. The method of claim 20, wherein the concentrated aqueous stream has a higher concentration of solubilized ions than the aqueous feed stream.
23. The method of claim 20, wherein the draw inlet stream has a higher osmotic pressure than an osmotic pressure of the aqueous feed stream.
24. The method of claim 20, wherein the draw inlet stream has a lower osmotic pressure than an osmotic pressure of the aqueous feed stream.
25. The method of claim 20, wherein, at at least one location on the osmotic membrane, a difference between an osmotic pressure on the first side of the osmotic membrane and an osmotic pressure on the second side of the osmotic membrane is less than 45 bar.
26. The method of claim 20, wherein the aqueous feed stream and the draw inlet stream are transported across the osmotic membrane in a counter-current configuration.
27. The method of claim 20, wherein the aqueous feed stream comprises Na+, Mg2+, Ca2+, Sr2+, Ba2+, Cl, carbonate anions, bicarbonate anions, sulfate anions, bisulfate anions, and/or dissolved silica.
28. The method of claim 20, wherein the draw inlet stream comprises Na+, Mg2+, Ca2+, Sr2+, Ba2+, and/or Cl.
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US11629072B2 (en) 2018-08-22 2023-04-18 Gradiant Corporation Liquid solution concentration system comprising isolated subsystem and related methods
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Citations (362)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US2151990A (en) 1938-02-19 1939-03-28 Shell Dev Recovery of organic compounds
US2606820A (en) 1947-09-25 1952-08-12 Dorr Co Apparatus for precipitation of solids from solutions and the like
US2606839A (en) 1951-03-21 1952-08-12 Dow Chemical Co Noncaking sea salt and method of producing the same
US2640018A (en) 1949-07-25 1953-05-26 Signal Oil & Gas Co Method of steam distillation
GB821939A (en) 1954-12-23 1959-10-14 Gerolamo Nossardi Method of and installation for the continuous extraction of magnesium with milk of lime from sea waters and the like
US2997856A (en) 1959-03-06 1961-08-29 John W Pike Method and apparatus for producing fresh water from saline water
US3032482A (en) 1959-04-02 1962-05-01 Richard W Shoemaker Process of recovering fresh water from salt water with a hot heavy material
US3042606A (en) 1960-05-31 1962-07-03 Grace W R & Co Descaling sea water
US3080302A (en) 1958-11-04 1963-03-05 Submerged Comb Inc Process and apparatus for converting non-potable water to potable water
GB1013767A (en) 1962-04-18 1965-12-22 Aqua Chem Inc Method and apparatus for purifying liquids
US3236747A (en) 1962-02-21 1966-02-22 Halcon International Inc Process for separating volatile material from a liquid mixture by a series of vaporization stages
GB1036920A (en) 1963-12-20 1966-07-20 Norris Bros Ltd Improvements in or relating to the production of potable water from sea water
US3331773A (en) 1966-07-22 1967-07-18 Grace W R & Co Process for inhibiting precipitation in water
US3454490A (en) 1966-08-10 1969-07-08 Atomic Energy Commission Concentration of ions using ion selective membranes
FR1582201A (en) 1968-07-24 1969-09-26
US3472766A (en) 1968-01-10 1969-10-14 Dow Chemical Co Separatory process utilizing a permeable polyamide membrane having poly (oxyethylene) grafts
US3475331A (en) 1968-02-23 1969-10-28 Dow Chemical Co Permeability separatory apparatus and process of making and using same
US3489652A (en) 1966-04-18 1970-01-13 American Mach & Foundry Desalination process by multi-effect,multi-stage flash distillation combined with power generation
US3625761A (en) 1969-12-23 1971-12-07 Texaco Inc Method for the treatment of alkaline earth metal sulfate scale
US3630378A (en) 1968-05-24 1971-12-28 Dow Chemical Co Novel water treating and storage apparatus
US3725209A (en) 1970-08-11 1973-04-03 F Rosa Centrifugal distillation system
DE2145861C2 (en) 1971-09-14 1973-06-07 Preussag Ag, 3000 Hannover Process and device for the preparation of recent colorful and precious metal-containing sea sludge by leaching using chlorine gas and metal clones
GB1320429A (en) 1970-12-10 1973-06-13 Israel Prime Ministers Office Process and apparatus for reverse osmosis
US3906250A (en) 1973-07-03 1975-09-16 Univ Ben Gurion Method and apparatus for generating power utilizing pressure-retarded-osmosis
US3922154A (en) 1972-09-11 1975-11-25 Agency Ind Science Techn Method for purification of sodium hydroxide
US3926739A (en) 1973-08-15 1975-12-16 Hitachi Ltd Multiple-effect multi-stage flash evaporation process and apparatus for demineralizing water
GB1444241A (en) 1972-08-08 1976-07-28 Tabata H Preparation of freshwater from sea water
US4062197A (en) 1976-07-09 1977-12-13 Hester Jarrett C Absorption heating-cooling system
US4105547A (en) 1974-12-23 1978-08-08 Alfa-Laval Ab Filtering process
US4156645A (en) 1973-07-26 1979-05-29 Desalination Systems Inc. Conversion of sea water by reverse osmosis
US4224148A (en) 1975-07-18 1980-09-23 Lindman William E Galvanic flow system for joint particulate recovery and liquid purification
JPS55147199A (en) 1979-05-07 1980-11-15 Shigeo Maekawa Recovering method for fresh water and solid matter from seawater containing mud or muddy water
US4251367A (en) 1979-01-25 1981-02-17 Waste Conversion Technology, Inc. Wastewater treatment
US4312755A (en) 1979-06-29 1982-01-26 Dow Corning Corporation Reverse osmosis system
US4334886A (en) 1978-02-24 1982-06-15 Katsuhiko Tani Method of manufacturing table salt
US4358377A (en) 1980-09-02 1982-11-09 The Dow Chemical Company Shear-vectoring design for composite casing end and removable, pressure-locking closure therefor
EP0070059A1 (en) 1981-07-10 1983-01-19 Nederlandse Organisatie voor toegepast-natuurwetenschappelijk onderzoek TNO Method and apparatus for concentrating solutions by means of reverse osmosis
US4452696A (en) 1981-04-06 1984-06-05 Fernand Lopez Reverse-osmosis apparatus for producing fresh water from seawater
US4478719A (en) 1979-11-22 1984-10-23 Helmut Michele Method and apparatus for the separation of fluids by permeation
US4511436A (en) 1982-05-24 1985-04-16 D.V.T. Buro Fur Anwendung Deutscher Verfahrenstechnik H. Morsy Apparatus for the desalination of sea water
FR2561637A1 (en) 1984-03-20 1985-09-27 Guiffray Michel Process and device for producing distilled water from seawater
US4563337A (en) 1982-08-13 1986-01-07 General Electric Company Method and apparatus for continuous ion exchange
US4574049A (en) 1984-06-04 1986-03-04 Arrowhead Industrial Water, Inc. Reverse osmosis system
US4576724A (en) 1981-06-25 1986-03-18 Colman Derek A Cyclone separator
EP0207390A1 (en) 1985-06-22 1987-01-07 BASF Aktiengesellschaft Process for the recovery of amine and metal compounds in the preparation of polyphenylene ether
US4652373A (en) 1986-02-21 1987-03-24 The Dow Chemical Company Tubesheet for spiral wound hollow fiber permeator
US4704324A (en) 1985-04-03 1987-11-03 The Dow Chemical Company Semi-permeable membranes prepared via reaction of cationic groups with nucleophilic groups
US4708805A (en) 1986-11-24 1987-11-24 Muhala Thomas F D Barium sulfate removal and anti-deposition compositions and process of use therefor
EP0253287A1 (en) 1986-07-15 1988-01-20 The Dow Chemical Company Combined membrane and sorption process for selective ion removal
US4735722A (en) 1987-06-15 1988-04-05 Krepak John C Desalination of seawater or brackish water
US4755298A (en) 1986-12-04 1988-07-05 The Dow Chemical Company Process for removing boron ions from aqueous solutions
US4765897A (en) 1986-04-28 1988-08-23 The Dow Chemical Company Polyamide membranes useful for water softening
US4769148A (en) 1987-11-18 1988-09-06 The Dow Chemical Company Novel polyamide reverse osmosis membranes
US4770775A (en) 1985-10-10 1988-09-13 Fernand Lopez Apparatus for the production of fresh water from sea water by reverse osmosis
US4812238A (en) 1987-01-15 1989-03-14 The Dow Chemical Company Membranes prepared via reaction of diazonium compounds or precursors
US4824574A (en) 1986-04-28 1989-04-25 The Dow Chemical Company Novel water softening process using membranes
US4828700A (en) 1987-07-20 1989-05-09 The Dow Chemical Company Rejection enhancing coatings for reverse osmosis membranes
US4832115A (en) 1986-07-09 1989-05-23 Albers Technologies Corporation Method and apparatus for simultaneous heat and mass transfer
US4839203A (en) 1985-04-03 1989-06-13 The Dow Chemical Company Semi-permeable membranes prepared via reaction of cationic groups with nucleophilic groups
US4843828A (en) 1985-10-04 1989-07-04 The Boc Group, Plc Liquid-vapor contact method and apparatus
US4859338A (en) 1987-08-06 1989-08-22 Thyssen Edelstahlwerke Ag Filter for small particles
US4859384A (en) 1987-11-18 1989-08-22 Filmtec Corp. Novel polyamide reverse osmosis membranes
US4894165A (en) 1987-07-20 1990-01-16 The Dow Chemical Company Rejection enhancing coatings for reverse osmosis membranes
US4909943A (en) 1987-07-20 1990-03-20 The Dow Chemical Company Rejection enhancing coatings for reverse osmosis membranes
US4927540A (en) 1986-09-04 1990-05-22 The Dow Chemical Company Ionic complex for enhancing performance of water treatment membranes
US4941972A (en) 1984-12-06 1990-07-17 The Dow Chemical Company Chlorine-stable membrane compositions
US4944882A (en) 1989-04-21 1990-07-31 Bend Research, Inc. Hybrid membrane separation systems
US4956157A (en) 1989-02-20 1990-09-11 Atsushi Nasu Process for separating salts in seawater
US4957817A (en) 1988-11-25 1990-09-18 The Dow Chemical Film, fiber, and microporous membranes of poly(etheretherketone)dissolved in high boiling point polar organic solvents
US4959237A (en) 1989-06-07 1990-09-25 E. I. Du Pont De Nemours And Company Reverse osmosis concentration of juice products with improved flavor
US4973201A (en) 1990-03-09 1990-11-27 Mobil Oil Corporation Method for removing scale and radioactive material from earth
US4980077A (en) 1989-06-22 1990-12-25 Mobil Oil Corporation Method for removing alkaline sulfate scale
US4980063A (en) 1989-01-27 1990-12-25 The Dow Chemical Company Compositions useful for preparing cellulose ester membranes for liquid separations
US4981593A (en) 1986-09-16 1991-01-01 Commonwealth Scientific And Industrial Research Organisation Sewage treatment
US4992485A (en) 1988-10-11 1991-02-12 The Dow Chemical Company Microporous peek membranes and the preparation thereof
US5015391A (en) 1989-12-12 1991-05-14 Betz Laboratories, Inc. Silicate coagulant aid for treatment of oily wastewaters
US5053132A (en) 1985-10-22 1991-10-01 The Trustees Of The Stevens Institute Of Technology Asymmetrically-wettable porous membrane
US5096590A (en) 1989-06-19 1992-03-17 Director Of National Food Research Institute, Ministry Of Agriculture, Forestry And Fisheries Concentration of solution by the reverse osmosis process
US5123481A (en) 1986-07-09 1992-06-23 Walter F. Albers Method and apparatus for simultaneous heat and mass transfer
US5167828A (en) 1991-10-07 1992-12-01 Nalco Chemical Company Phosphinate-containing polymers for controlling scale in underground petroleum-containing formations and equipment associated therewith
US5190656A (en) 1989-04-03 1993-03-02 Mobil Oil Corporation Method for removing scale via a liquid membrane in combination with an amino carboxylic acid and a catalyst
US5207916A (en) 1992-05-20 1993-05-04 Mesco, Inc. Reverse osmosis system
US5225087A (en) 1991-05-10 1993-07-06 Westinghouse Electric Corp. Recovery of EDTA from steam generator cleaning solutions
US5238574A (en) 1990-06-25 1993-08-24 Kawasaki Jukogyo Kabushiki Kaisha Method and apparatus having reverse osmosis membrane for concentrating solution
US5250185A (en) 1992-05-01 1993-10-05 Texaco Inc. Reducing aqueous boron concentrations with reverse osmosis membranes operating at a high pH
US5282995A (en) 1989-04-03 1994-02-01 Mobil Oil Corporation Composition for removing an alkaline earth metal sulfate scale
US5328616A (en) 1992-11-20 1994-07-12 Monsanto Company Methods and apparatus for treating electroless plating baths
EP0623561A1 (en) 1993-04-05 1994-11-09 Electricite De France Process and device for decontaminating a liquid effluent containing ionic metals
US5425902A (en) 1993-11-04 1995-06-20 Tom Miller, Inc. Method for humidifying air
US5453205A (en) 1991-05-29 1995-09-26 Modern Environmental Service Trust Treatment of emulsions
WO1995027683A1 (en) 1994-04-06 1995-10-19 Zenon Environmental, Inc. Microfiltration enhanced reverse osmosis for water treatment
US5464540A (en) 1993-12-09 1995-11-07 Bend Research, Inc. Pervaporation by countercurrent condensable sweep
US5490937A (en) 1990-09-17 1996-02-13 Genentech, Inc. Tangential flow filtration process and apparatus
US5503750A (en) 1993-10-04 1996-04-02 Russo, Jr.; Lawrence J. Membrane-based process for the recovery of lactic acid by fermentation of carbohydrate substrates containing sugars
US5656161A (en) 1993-04-20 1997-08-12 Ionics, Incorporated Salt basket for crystallizer and method of use in zero liquid discharge industrial facilities
US5670053A (en) 1995-08-07 1997-09-23 Zenon Environmental, Inc. Purification of gases from water using reverse osmosis
US5840195A (en) 1995-05-01 1998-11-24 Omnium De Traitement Et De Valorisation Method and installation for treating an untreated flow by simple sedimentation after ballasting with fine sand
US5873260A (en) 1997-04-02 1999-02-23 Linhardt; Hans D. Refrigeration apparatus and method
WO2000000273A1 (en) 1998-06-29 2000-01-06 Hw Process Technologies, Inc. Method of removing sulfate and/or metal ions from waters or wastewaters
US6056878A (en) 1998-08-03 2000-05-02 E-Cell Corporation Method and apparatus for reducing scaling in electrodeionization systems and for improving efficiency thereof
US6062070A (en) 1996-10-29 2000-05-16 Drexelbrook Controls, Inc. Method and apparatus for the sonic measurement of sludge and clarity conditions during the treatment of waste water
US6113797A (en) 1996-10-01 2000-09-05 Al-Samadi; Riad A. High water recovery membrane purification process
US6146525A (en) 1998-02-09 2000-11-14 Cycteck Environmental, Inc. Apparatus and methods for separating particulates from a particulate suspension in wastewater processing and cleaning
US6187200B1 (en) 1994-10-12 2001-02-13 Toray Industries, Inc. Apparatus and method for multistage reverse osmosis separation
US6190558B1 (en) 1999-04-01 2001-02-20 Nimbus Water Systems, Inc. Reverse osmosis purification system
US6190556B1 (en) 1998-10-12 2001-02-20 Robert A. Uhlinger Desalination method and apparatus utilizing nanofiltration and reverse osmosis membranes
WO2001014256A1 (en) 1999-08-20 2001-03-01 L.E.T. Leading Edge Technologies Limited A salt water desalination process using ion selective membranes
US6270671B1 (en) 1999-01-08 2001-08-07 United States Filter Corporation Method and apparatus for microfiltration
US6299766B1 (en) 2000-07-06 2001-10-09 Clark Permar Reverse osmosis filtering apparatus with concentrate dilution
US6319409B1 (en) 1998-09-11 2001-11-20 Fuji Jukogyo Kabushiki Kaisha Process for treating waste water containing cutting oil
JP2002001068A (en) 2000-06-21 2002-01-08 Kurita Water Ind Ltd Method and apparatus for membrane separation
WO2002032813A1 (en) 2000-10-21 2002-04-25 Pb Power Ltd. Process and plant for multi-stage flash desalination of water
US6416668B1 (en) 1999-09-01 2002-07-09 Riad A. Al-Samadi Water treatment process for membranes
US6423235B1 (en) 1999-08-18 2002-07-23 Nittetu Chemical Engineering Ltd. Column gas-liquid contacting apparatus and its use thereof
US20020108907A1 (en) 1996-01-17 2002-08-15 Van Reis Robert D. Tangential-flow filtration system
US6508936B1 (en) 1997-10-01 2003-01-21 Saline Water Conversion Corporation Process for desalination of saline water, especially water, having increased product yield and quality
US6547965B1 (en) 1998-02-27 2003-04-15 Nate International Large tube assemblies for reverse osmosis
US20030106860A1 (en) 2001-11-09 2003-06-12 Guy Peloquin Apparatus for and method of settling of mineral slurries
US6582605B2 (en) 2000-07-07 2003-06-24 Ionics, Incorporated Method of treating industrial waste waters
US20030132166A1 (en) 2002-01-15 2003-07-17 Paul Rey Method of treating mine drainage
US6699369B1 (en) 2001-08-10 2004-03-02 Aquasonics International Apparatus and method for thermal desalination based on pressurized formation and evaporation of droplets
US6730234B2 (en) 2001-03-15 2004-05-04 Tetra Technologies, Inc. Method for regeneration of used halide fluids
GB2395946A (en) 2002-12-05 2004-06-09 Thomas Altmann Extracting sodium chloride from seawater, using nanofiltration
US6783682B1 (en) 1999-08-20 2004-08-31 L.E.T., Leading Edge Technologies Limited Salt water desalination process using ion selective membranes
US20040187897A1 (en) 2002-12-18 2004-09-30 Andy Kenowski Monitoring device and method for operating clean-in-place system
US6817476B2 (en) 2003-01-31 2004-11-16 Aerex Industries, Inc. Water clarification system
US20050023222A1 (en) 2003-05-30 2005-02-03 Brian Baillie Filtration apparatus and method
WO2005012185A1 (en) 2003-07-30 2005-02-10 University Of Surrey Solvent removal process
CN1623936A (en) 2004-10-26 2005-06-08 南京工业大学 Technology for recovering ash water of coal-fired power plant and system of sealing circulating for recovering thereof
US6919000B2 (en) 2002-12-17 2005-07-19 University Of Florida Diffusion driven desalination apparatus and process
US7022240B2 (en) 2003-01-15 2006-04-04 Hart Resource Technologies, Inc. Method for on-site treatment of oil and gas well waste fluids
US7048852B2 (en) 2002-10-31 2006-05-23 Infilco Degremont, Inc. Method and apparatus for treating water or wastewater to reduce organic and hardness contamination
US20060127550A1 (en) 2001-01-16 2006-06-15 Kagome Kabushiki Kaisha Apparatus for concentrating processed vegetable and fruit products by reverse osmosis
US20060144787A1 (en) 2005-01-06 2006-07-06 Eet Corporation Integrated electro-pressure membrane deionization system
US20060150892A1 (en) 2003-04-29 2006-07-13 Akzo Nobel N.V. Processes Involving the Use of Antisolvent Crystallisation
US20060157409A1 (en) 2005-01-14 2006-07-20 Saline Water Conversion Corporation (Swcc) Optimal high recovery, energy efficient dual fully integrated nanofiltration seawater reverse osmosis desalination process and equipment
US20060157410A1 (en) 2005-01-14 2006-07-20 Saline Water Conversion Corporation (Swcc) Fully integrated NF-thermal seawater desalination process and equipment
CN1835892A (en) 2003-08-17 2006-09-20 艾维·艾弗雷提 Continuous closed-circuit desalination apparatus with single container
US7115670B2 (en) 2001-05-25 2006-10-03 Bp Exploration Operating Company Limited Fischer-Tropsch synthesis process
US7141171B2 (en) 2004-05-21 2006-11-28 Wisconsin Alumni Research Foundation Membrane cascade-based separation
US20070012556A1 (en) 2003-12-02 2007-01-18 Lum Gary W Water processing apparatus
US20070068791A1 (en) 2003-12-02 2007-03-29 Thom Douglas M Automated water processing control system
US20070080113A1 (en) 2002-05-02 2007-04-12 City Of Long Beach Two stage nanofiltration seawater desalination system
EP1775267A2 (en) 2005-06-23 2007-04-18 Esposito Servizi Ecologici s.r.l. Plant and process for the recycling of sweepings, water purifier wastes and the like
US20070084713A1 (en) 2005-10-19 2007-04-19 Deep Richard J Water purification system
US20070102359A1 (en) 2005-04-27 2007-05-10 Lombardi John A Treating produced waters
US7225620B2 (en) 2002-12-17 2007-06-05 University Of Florida Research Foundation, Inc. Diffusion driven water purification apparatus and process
US20070131428A1 (en) 2005-10-24 2007-06-14 Willem Cornelis Den Boestert J Methods of filtering a liquid stream produced from an in situ heat treatment process
CN100999364A (en) 2006-05-16 2007-07-18 葛文宇 Comprehensive utilization high advantage zero discharge seawater desalination production technology
US20070181480A1 (en) 2006-02-09 2007-08-09 Dong-Won Lee Water filtering device
US20070235391A1 (en) 2006-04-11 2007-10-11 Sorbwater Technology As Method for removal of materials from a liquid stream
CN101056693A (en) 2004-09-13 2007-10-17 南卡罗来纳大学 Water desalination process and apparatus
US20070246406A1 (en) 2006-03-31 2007-10-25 Dibel Kevin R Tangential flow filtration apparatuses, systems, and processes for the separation of compounds
WO2007128062A1 (en) 2006-05-05 2007-11-15 Newcastle Innovation Limited Desalination method and apparatus
WO2007132477A1 (en) 2006-05-11 2007-11-22 Raman Ahilan A pretreatment process for the saline water feeds of desalination plants
WO2007138327A1 (en) 2006-06-01 2007-12-06 Natco Uk Limited Method of providing a supply of water of controlled salinity and water treatment system
US7306437B2 (en) 2004-08-10 2007-12-11 Leif Hauge Pressure exchanger
WO2007144591A1 (en) 2006-06-14 2007-12-21 Vws Westgarth Limited Apparatus and method for treating injection fluid
US7316080B1 (en) 2004-05-27 2008-01-08 Solution Dynamics, Llc Methodology and apparatus to reduce fuel consumption in conveyor dryers and ovens
US20080023333A1 (en) 2006-07-17 2008-01-31 Brendan Johnson Microscale capacitive deionization apparatus
US20080073200A1 (en) 2006-09-22 2008-03-27 Altela, Inc. Novel enhanced systems, processes and methodologies for producing clean water and products thereby
US20080102119A1 (en) 2006-11-01 2008-05-01 Medtronic, Inc. Osmotic pump apparatus and associated methods
US20080116134A1 (en) 2004-01-30 2008-05-22 Cartwright Peter S Brine-Conserving Nanofiltration Water Softener System
US20080121585A1 (en) 2006-11-27 2008-05-29 Mavis James D Water treatment using de-supersaturation
US20080164206A1 (en) 2007-01-10 2008-07-10 Southwest Turf Solutions, Inc. Method and apparatus for removing minerals from a water source
US20080237110A1 (en) 2004-05-21 2008-10-02 Wisconsin Alumni Research Foundation Membrane cascade-based separation
US20080245737A1 (en) 2007-04-03 2008-10-09 Siemens Water Technologies Corp. Method and system for providing ultrapure water
US20080277344A1 (en) 2007-05-11 2008-11-13 Arup K. Sengupta Brackish and sea water desalination using a hybrid ion exchange-nanofiltration process
WO2008137082A1 (en) 2007-05-02 2008-11-13 Yale University Method for designing membranes for osmotically driven membrane processes
US7459084B2 (en) 2001-06-22 2008-12-02 Petro Sep International Ltd. Membrane-assisted fluid separation apparatus and method
US7465376B2 (en) 2001-02-22 2008-12-16 Susanne Neubert Method and device for treating liquids
US20090020289A1 (en) 2005-05-06 2009-01-22 University Of Surrey Secondary oil recovery
US20090032446A1 (en) 2007-08-01 2009-02-05 Triwatech, L.L.C. Mobile station and methods for diagnosing and modeling site specific effluent treatment facility requirements
US7510656B2 (en) 2006-09-01 2009-03-31 Anticline Disposal, Llc Waste water treatment method
CN101397152A (en) 2007-09-28 2009-04-01 旭化成化学株式会社 Brine treatment method
US7520993B1 (en) 2007-12-06 2009-04-21 Water & Power Technologies, Inc. Water treatment process for oilfield produced water
US20090101490A1 (en) 2005-07-06 2009-04-23 Sylvan Source, Inc. Water Purification System
US20090101587A1 (en) 2007-10-22 2009-04-23 Peter Blokker Method of inhibiting scale formation and deposition in desalination systems
CN101417208A (en) 2008-11-14 2009-04-29 清华大学 Extractive agent recovering method in water phase using film isolation technique
US7527726B2 (en) 2006-01-25 2009-05-05 Q'max Solutions Inc. Fluid treatment apparatus
US20090127210A1 (en) 2007-11-20 2009-05-21 Swisher Anthony E Method and apparatus for water remediation
US20090173096A1 (en) 2008-01-08 2009-07-09 Calvin Wade Wohlert Methodology for converting existing packaged rooftop air conditioning units to be served from a centralized water cooled refrigeration and/or heat pump system
US20090173690A1 (en) 2008-01-04 2009-07-09 Fluid Equipment Development Company, Llc Batch-operated reverse osmosis system
US20090218210A1 (en) 2005-10-14 2009-09-03 Laura Demmons Energy-efficient distillation system
US7597784B2 (en) 2002-11-13 2009-10-06 Deka Products Limited Partnership Pressurized vapor cycle liquid distillation
US20090277641A1 (en) 2008-05-07 2009-11-12 Harold Walters Methods of using a lower-quality water for use as some of the water in the forming and delivering of a treatment fluid into a wellbore
US20090277640A1 (en) 2008-05-07 2009-11-12 Jonn Thompson Methods of using a higher-quality water with an unhydrated hydratable additive allowing the use of a lower-quality water as some of the water in the forming and delivering of a treatment fluid into a wellbore
US20090277634A1 (en) 2008-05-07 2009-11-12 Leonard Case Methods of pumping fluids having different concentrations of particulate with different concentrations of hydratable additive to reduce pump wear and maintenance in the forming and delivering of a treatment fluid into a wellbore
US20090308820A1 (en) 2006-03-03 2009-12-17 Eugene Thiers Contaminant Prevention
CN101636354A (en) 2006-10-10 2010-01-27 得克萨斯A&M大学系统 Desalination system
US20100032377A1 (en) 2008-06-13 2010-02-11 Calvin Wade Wohlert Apparatus and methods for solution processing using reverse osmosis
WO2010026589A1 (en) 2008-09-04 2010-03-11 I.D.E. Technologies Ltd. Improved water desalination system
US7726398B2 (en) 2005-06-16 2010-06-01 Bp Exploration Operating Company Limited Water flooding method
US7727400B2 (en) 2005-09-23 2010-06-01 Michael Flynn Low water recovery rate desalination system and method
CN101717161A (en) 2009-10-30 2010-06-02 葛文宇 Production process for achieving hundred-percent comprehensive utilization and zero emission by recycling and extracting seawater
US20100132386A1 (en) 2008-12-02 2010-06-03 Xergy Incorporated Electrochemical Compressor and Refrigeration System
US7731847B2 (en) 2007-05-25 2010-06-08 Huy Ton That Submersible reverse osmosis desalination apparatus and method
US20100163472A1 (en) 2007-03-21 2010-07-01 Sylvan Source, Inc. Water purification system
US20100163471A1 (en) 2008-12-30 2010-07-01 Irving Elyanow Water desalination plant and system for the production of pure water and salt
US20100234795A1 (en) 2006-08-16 2010-09-16 Wallenaes Anders System and method for regeneration of a fluid
US20100242995A1 (en) 2009-03-26 2010-09-30 General Electric Company Method for removing ionic species from desalination unit
WO2010118425A1 (en) 2009-04-10 2010-10-14 Sylvan Source, Inc. Method and system for reduction of scaling in purification of aqueous solutions
US7815804B2 (en) 2006-12-12 2010-10-19 Otv Sa S.A. Method for treating wastewater or produced water
WO2010122336A2 (en) 2009-04-21 2010-10-28 Abdulsalam Al-Mayahi Water treatment
US7824552B2 (en) 2007-09-05 2010-11-02 Halliburton Energy Services, Inc. Mobile systems and methods of sufficiently treating water so that the treated water may be utilized in well-treatment operations
US20100282675A1 (en) 2009-05-08 2010-11-11 Lehigh University System and method for reversible cation-exchange desalination
WO2010131251A2 (en) 2009-05-13 2010-11-18 Renewed Water Minerals Ltd. Separation of mg2+ ions from sea-and brackish water for the purpose of re-mineralization of water and wastewater
WO2010135561A2 (en) 2009-05-20 2010-11-25 Aquatech International Corporation Method for treatment and purification of seawater to recover high purity sodium chloride for industrial usage
US20100294718A1 (en) 2007-06-08 2010-11-25 Swiss Fresh Water Sa Liquid purification system using a medium pressure membrane
US20100314238A1 (en) 2010-04-30 2010-12-16 Sunlight Photonics Inc. Hybrid solar desalination system
US20110017677A1 (en) 2009-06-04 2011-01-27 Evans Thomas S Oil field water recycling system and method
US20110024354A1 (en) 2009-07-30 2011-02-03 General Electric Company Desalination system and method
US20110056878A1 (en) 2009-09-10 2011-03-10 Takeshi Matsushiro Membrane filtration system
US20110056822A1 (en) 2009-09-04 2011-03-10 Massachusetts Institute Of Technology Water Separation Under Reduced Pressure
CN102036739A (en) 2008-11-17 2011-04-27 凯米涛弗特公司 Recovery of lithium from aqueous solutions
US20110108484A1 (en) 2008-07-09 2011-05-12 I.D.E. Technologies Ltd. Method of improving performance of a reverse osmosis system for seawater desalination, and modified reverse osmosis system obtained thereby
US20110120157A1 (en) 2009-10-30 2011-05-26 Calvin Wohlert Absorption refrigeration cycles; apparatus; and, methods
US7950921B1 (en) 2007-07-20 2011-05-31 Solution Dynamics, Llc Method and apparatus for cooling the underside of kiln cars
US20110155666A1 (en) 2009-12-30 2011-06-30 Chevron U.S.A. Inc. Method and system using hybrid forward osmosis-nanofiltration (h-fonf) employing polyvalent ions in a draw solution for treating produced water
US20110180479A1 (en) 2010-01-27 2011-07-28 Milton Roy Company Zero liquid discharge water treatment system and method
US20110198285A1 (en) 2010-02-17 2011-08-18 Katana Energy Llc Zero Discharge Water Desalination Plant With Minerals Extraction Integrated With Natural Gas Combined Cycle Power Generation
US20110215039A1 (en) 2010-03-04 2011-09-08 Terragroup Corporation Lightweight modular water purification system with reconfigurable pump power options
US20110233137A1 (en) 2004-12-06 2011-09-29 Cath Tzahi Y Systems and methods for purification of liquids
US20110257788A1 (en) 2007-08-01 2011-10-20 Wiemers Reginald A Mobile station and methods for diagnosing and modeling site specific full-scale effluent treatment facility requirements
CN102258942A (en) 2010-05-26 2011-11-30 覃正元 Three-stage reverse osmosis
US20110303607A1 (en) 2010-06-15 2011-12-15 General Electric Company Seawater desalination plant and production of high purity salt
US20110306525A1 (en) 2009-02-13 2011-12-15 Dirk Jacob Lighthelm Aqueous displacement fluid injection for enhancing oil recovery from an oil bearing formation
US20120012005A1 (en) 2010-07-16 2012-01-19 Solution Dynamics Regenerative Dryers With A Bypass
US20120012511A1 (en) 2010-07-14 2012-01-19 Korea Institute Of Machinery & Materials Apparatus for osmotic power generation and desalination using salinity difference
US20120037568A1 (en) 2010-08-10 2012-02-16 Siemens Industry, Inc. Controlled method of minimizing radioactive sludge generation in post stimulation flowback and/or produced water treatment from a saltwater, oil and/or gas well
US8119007B2 (en) 2009-11-25 2012-02-21 Massachusetts Institute Of Technology Water desalination using directional solvent extraction
CN102363101A (en) 2011-11-14 2012-02-29 天津森诺过滤技术有限公司 Submerged membrane filtration system and process for removing suspended solid from phosphating liquid
US20120067819A1 (en) 2009-10-28 2012-03-22 Oasys Water, Inc. Osmotically driven membrane processes and systems and methods for draw solute recovery
US20120067820A1 (en) 2010-09-21 2012-03-22 Water Standard Company Llc Method and apparatus for dynamic, variable-pressure, customizable, membrane-based water treatment for use in improved hydrocarbon recovery operations
US8147696B1 (en) 2006-09-19 2012-04-03 Pandya Ken V High-efficiency water-softening process
US20120091061A1 (en) 2011-07-03 2012-04-19 King Abdulaziz City for Organization Name Science and Technology "KACST" Apparatus and process for desalination of brackish water using pressure retarded osmosis
US20120090833A1 (en) 2010-10-15 2012-04-19 Shell Oil Company Water injection systems and methods
US20120125603A1 (en) 2010-11-19 2012-05-24 Willingham Thomas W Systems and Methods For Enhanced Waterfloods
US20120125611A1 (en) 2009-06-25 2012-05-24 Shell Internationalale Research Maatschappij Water injection systems and methods
US8197693B2 (en) 2011-07-03 2012-06-12 King Abdulazia City for Science and Technology (KACST) Apparatus and process for producing electricity using pressure retarded osmosis during desalination of sea water
US20120145635A1 (en) 2010-10-14 2012-06-14 Lucas Iii Arthur L Treatment of waters with multiple contaminants
US20120199524A1 (en) 2011-02-09 2012-08-09 Ccs Midstream Services, Llc. Method and apparatus for treating well flow-back and produced water or other wastewater
US20120205307A1 (en) 2009-10-27 2012-08-16 Vws Westgarth Limited Fluid treatment apparatus and method
US8252092B2 (en) 2009-10-05 2012-08-28 Massachusetts Institute Of Technology Water separation under varied pressure
US20120227975A1 (en) 2009-11-02 2012-09-13 Ayirala Subhash Chandra Bose Water injection systems and methods
US20120234765A1 (en) 2011-03-15 2012-09-20 Lehigh University Method of treatment of produced water and recovery of important divalent cations
US20120234664A1 (en) 2009-10-28 2012-09-20 Surrey Aquatechnology Ltd. Thermal Desalination
WO2012138502A1 (en) 2011-04-06 2012-10-11 Ysawyer John E Treatment of waters with multiple contaminants
WO2012142396A1 (en) 2011-04-14 2012-10-18 Basf Se Method of dissolving and/or inhibiting the deposition of scale on a surface of a system
US20120267307A1 (en) 2011-04-25 2012-10-25 Mcginnis Robert L Osmotic separation systems and methods
US20120273417A1 (en) 2009-10-28 2012-11-01 Oasys Water, Inc. Forward osmosis separation processes
US20120279396A1 (en) 2011-03-15 2012-11-08 Mks Instruments, Inc. System to remove Dissolved Gases Selectively from Liquids
US20120285886A1 (en) 2009-11-25 2012-11-15 I.D.E. Technologies Ltd. Reciprocal enhancement of reverse osmosis and forward osmosis
US20120292259A1 (en) 2011-05-17 2012-11-22 High Sierra Energy, LP System and method for treatment of produced waters containing gel
WO2012159203A1 (en) 2011-05-24 2012-11-29 Saltworks Technologies Inc. Method, apparatus and system for concentrating solutions using evaporation
CA2779732A1 (en) 2011-06-10 2012-12-10 Aqua-Pure Ventures Inc. Mobile clarifier and sludge dewatering system for onsite waste water treatment
US20120318729A1 (en) 2009-12-03 2012-12-20 Yale University Office Of Cooperative Research High Flux Thin-Film Composite Forward Osmosis and Pressure-Retarded Osmosis Membranes
US20130008079A1 (en) 2011-07-05 2013-01-10 Dr. Deborah Duen Ling Chung Coagulation of oil in water and the resulting floating semisolid complex
WO2013012548A1 (en) 2011-07-20 2013-01-24 Cameron International Corporation System to provide a supply of controlled salinity water for enhanced oil recovery
KR101229482B1 (en) 2012-07-12 2013-02-04 한국기계연구원 Apparatus and method for hybrid desalination
US20130043190A1 (en) 2011-08-17 2013-02-21 Riad A. Al-Samadi High Recovery Drinking Water Process
US20130056193A1 (en) 2010-01-12 2013-03-07 Sylvan Source, Inc. Heat transfer interface
WO2013037047A1 (en) 2011-09-15 2013-03-21 Saltworks Technologies Inc. Method, apparatus and system for desalinating saltwater
US20130075940A1 (en) 2011-09-23 2013-03-28 King Fahd University Of Petroleum And Minerals Bubble-Column Vapor Mixture Condenser
US20130075098A1 (en) 2011-09-27 2013-03-28 Fluor Technologies Corporation Methods for treatment and use of produced water
US20130087501A1 (en) 2011-10-06 2013-04-11 General Electric Compay Seawater desalination process
US20130092626A1 (en) 2006-10-30 2013-04-18 Perlemax Ltd Bubble generation for aeration and other purposes
US20130092622A1 (en) 2011-04-01 2013-04-18 Millipore Corporation Nanofiber containing composite membrane structures
US20130105323A1 (en) 2011-10-27 2013-05-02 David J. Averbeck Ion Removal Using a Capacitive Deionization System
WO2013078124A1 (en) 2011-11-23 2013-05-30 Advanced Aqua Group Water conversion system
US8469092B2 (en) 2007-07-19 2013-06-25 Shell Oil Company Water processing system and methods
KR20130074104A (en) 2011-12-26 2013-07-04 한국건설기술연구원 Combination-type desalination apparatus of forward osmosis(fo) and reverse osmosis(ro) using multi-water source as feed water and sea water as draw solution, and system and method for controlling membrane process for the same
US20130186822A1 (en) 2012-01-20 2013-07-25 Hydration Systems, Llc Low energy forward osmosis membrane water processing system
US8496234B1 (en) 2012-07-16 2013-07-30 Massachusetts Institute Of Technology Thermodynamic balancing of combined heat and mass exchange devices
US20130193074A1 (en) 2010-05-13 2013-08-01 Clean Teq Holdings Ltd. Water treatment process
US20130199921A1 (en) 2012-02-07 2013-08-08 Massachusetts Institute Of Technology Carrier-Gas Humidification-Dehumidification Using Heat-Transfer Members for Enhanced Heat Recovery
US20130213892A1 (en) 2011-12-22 2013-08-22 Water Standard Company (Mi) Method and control devices for production of consistent water quality from membrane-based water treatment for use in improved hydrocarbon recovery operations
US20130233786A1 (en) 2012-02-22 2013-09-12 Richard Paul Posa System and method for treating water
US20130240442A1 (en) 2012-03-16 2013-09-19 Ravi Chidambaran Process for purification of produced water
US20130256228A1 (en) 2012-03-30 2013-10-03 Hydration Systems, Llc Use of novel draw solutes and combinations thereof to improve performance of a forward osmosis system and process
WO2013158315A1 (en) 2012-04-18 2013-10-24 Hydration Systems, Llc Method for producing water for enhanced oil recovery
WO2013159220A1 (en) 2012-04-25 2013-10-31 Saltworks Technologies Inc. Modular humidification-dehumidification apparatus for concentrating solutions
WO2013172605A1 (en) 2012-05-15 2013-11-21 고려대학교 산학협력단 Low energy salt water desalination method and salt water desalination system using pressure retarded osmosis and reverse osmosis
CA2818055C (en) 2012-04-25 2013-11-26 Saltworks Technologies Inc. Modular humidification-dehumidification apparatus for concentrating solutions
US20130318743A1 (en) 2012-05-30 2013-12-05 GM Global Technology Operations LLC Check link assembly with adjustable detent feature
US20140008291A1 (en) 2011-01-25 2014-01-09 Nanyang Technological University Forward osmosis membrane and method of forming a forward osmosis membrane
CN103547798A (en) 2011-03-30 2014-01-29 东丽株式会社 Concentration difference power generation device and method for operating same
US8647477B2 (en) 2011-02-15 2014-02-11 Massachusetts Institute Of Technology High-efficiency thermal-energy-driven water purification system
US20140042058A1 (en) 2012-08-09 2014-02-13 Shell Oil Company Process for producing and separating oil
US20140041856A1 (en) 2012-08-09 2014-02-13 Shell Oil Company System for producing and separating oil
US20140042061A1 (en) 2012-08-13 2014-02-13 Enviro Water Minerals Company, Inc. Heating system for desalination
US20140061022A1 (en) 2008-12-15 2014-03-06 Water Desalination International, Inc. Water Desalination System
US20140069821A1 (en) 2012-05-23 2014-03-13 High Sierra Energy, LP System and method for treatment of produced waters
US8679347B2 (en) 2010-05-26 2014-03-25 Riad A. Al-Samadi Multi-use high water recovery process
US8695343B2 (en) 2009-12-04 2014-04-15 General Electric Company Economical and sustainable disposal of zero liquid discharge salt byproduct
WO2014058696A1 (en) 2012-10-10 2014-04-17 M-I L.L.C. Boron removal system and method
US20140116956A1 (en) 2012-10-28 2014-05-01 SYNCRUDE CANADA LTD. in trust for the owners of the Syncrude Project Fort McMurray Co-processing of fluid fine tailings and fresh oil sands tailings
DE102012017860A1 (en) 2012-09-11 2014-05-15 Peter Vinz Treatment method for enriching on separating mixture components from sewage liquid mixtures, involves depressurizing and re-introducing permeate from primary channel of first treatment zone into secondary channel of second treatment zone
WO2014088826A1 (en) 2012-12-07 2014-06-12 Aquatech International Corporation Water treatment process
US8771477B2 (en) 2008-09-17 2014-07-08 Sylvan Source, Inc. Large-scale water purification and desalination
US20140197022A1 (en) 2013-01-15 2014-07-17 King Abdulaziz City For Science And Technology Solar-powered humidification-dehumidification desalination system
US8794320B2 (en) 2006-03-27 2014-08-05 Shell Oil Company Water injection systems and methods
WO2014121153A2 (en) 2013-02-01 2014-08-07 Lake Country Fracwater Specialists, Llc Method and apparatus for treating natural gas and oil well waste waters for removal of contaminants and dissolved solids
US20140246368A1 (en) 2008-11-11 2014-09-04 P & Ls Holding Gmbh Membrane separation devices and water treatment plants
WO2014144778A1 (en) 2013-03-15 2014-09-18 Porifera, Inc. Advancements in osmotically driven membrane systems including multi-stage purification
US20140263055A1 (en) 2013-03-14 2014-09-18 Massachusetts Institute Of Technology Ion Sequestration for Scale Prevention in High-Recovery Desalination Systems
US20140263081A1 (en) 2011-09-09 2014-09-18 Sylvan Source,Inc. Industrial water purification and desalination
WO2014162094A2 (en) 2013-04-03 2014-10-09 Total Sa Production of injection water by coupling direct‑osmosis methods with other methods of filtration
US8889000B2 (en) 2011-09-15 2014-11-18 Storm Drain Technologies, Llc Apparatus, methods, and system for treatment of stormwater and waste fluids
US20140339162A1 (en) 2013-05-17 2014-11-20 Baker Hughes Incorporated Boron removal from oilfield water
WO2014188450A1 (en) 2013-05-23 2014-11-27 Council Of Scientific & Industrial Research Improved process to retain nutritious constituents in potable water obtained through desalination
US20140367871A1 (en) 2013-06-12 2014-12-18 King Fahd University Of Petroleum & Minerals Multi-Stage Bubble Column Humidifier
US20150014248A1 (en) 2013-07-15 2015-01-15 Hydration Systems, Llc Method and system for generating strong brines
US20150013987A1 (en) 2013-07-11 2015-01-15 Baker Hughes Incorporated Method for reducing sulfide in oilfield waste water and making treated water
WO2015021062A1 (en) 2013-08-05 2015-02-12 Gradiant Corporation Water treatment systems and associated methods
US20150053619A1 (en) 2013-08-21 2015-02-26 Baker Hughes Incorporated Process for Hardness and Boron Removal
US20150060360A1 (en) 2012-04-12 2015-03-05 Dxv Water Technologies, Llc Systems and methods of membrane separation
US8980100B2 (en) 2012-04-23 2015-03-17 Aquatech International Corporation Low energy reverse osmosis process
WO2015038983A2 (en) 2013-09-12 2015-03-19 Gradiant Corporation Systems including a condensing apparatus such as a bubble column condenser
US20150083577A1 (en) 2013-09-23 2015-03-26 Gradiant Corporation Desalination systems and associated methods
US20150083656A1 (en) 2010-01-14 2015-03-26 Bp Exploration Operating Company Limited Process of supplying water of controlled salinity
US8999172B1 (en) 2010-12-16 2015-04-07 Global Water Advisors, Inc. Selective removal of dissolved substances from aqueous solutions
US20150107841A1 (en) 2013-10-23 2015-04-23 Shell Oil Company Process for reducing viscosity of polymer-containing fluid produced in the recovery of oil
US20150107840A1 (en) 2013-10-23 2015-04-23 Shell Oil Company Process for recovery of oil from an oil-bearing formation
US9085971B2 (en) 2011-12-29 2015-07-21 Shell Oil Company Method and system for enhancing oil recovery (EOR) by injecting treated water into an oil bearing formation
US9206060B1 (en) 2015-05-22 2015-12-08 Basel Abusharkh Method for purifying liquids
US20150353397A1 (en) 2013-01-10 2015-12-10 Tzahi Y. Cath Water reuse system and method
US9221694B1 (en) 2014-10-22 2015-12-29 Gradiant Corporation Selective scaling in desalination water treatment systems and associated methods
US20160001235A1 (en) 2014-07-07 2016-01-07 E I Du Pont De Nemours And Company Filtration membranes
US9266748B1 (en) 2015-05-21 2016-02-23 Gradiant Corporation Transiently-operated desalination systems with heat recovery and associated methods
US9266762B2 (en) 2010-09-30 2016-02-23 General Electric Company Membrane filtration process with high water recovery
WO2016057764A1 (en) 2014-10-10 2016-04-14 Oasys Water, Inc. Osmotic separation systems and methods
US20160229705A1 (en) 2015-02-11 2016-08-11 Gradiant Corporation Methods and systems for producing treated brines for desalination
US20160244349A1 (en) 2015-02-11 2016-08-25 Gradiant Corporation Production of ultra-high-density brines
US9427705B1 (en) 2015-05-22 2016-08-30 Basel Abusharkh Method of solvent recovery from a dilute solution
US9428404B2 (en) 2011-10-04 2016-08-30 Massachusetts Institute Of Technology Water extraction using a directional solvent
US20160339354A1 (en) 2015-05-21 2016-11-24 Gradiant Corporation Transiently-operated desalination systems and associated methods
US20160339357A1 (en) 2015-05-21 2016-11-24 Gradiant Corporation Systems including an apparatus comprising both a humidification region and a dehumidification region with heat recovery and/or intermediate injection
US20160339356A1 (en) 2015-05-21 2016-11-24 Gradiant Corporation Systems including an apparatus comprising both a humidification region and a dehumidification region
US9550685B2 (en) 2008-09-04 2017-01-24 University Of Florida Research Foundation, Inc. Desalination apparatus and process
WO2017019944A1 (en) 2015-07-29 2017-02-02 Gradiant Corporation Osmotic desalination methods and associated systems
US20170036171A1 (en) 2014-04-23 2017-02-09 Massachusetts Institute Of Technology Liquid Purification System
US20170044033A1 (en) 2014-04-23 2017-02-16 Massachusetts Institute Of Technology Method and Apparatus for Partially Desalinating Produced Water to Form Extraction Fluid Used for Fossil Fuel Extraction
WO2017030932A1 (en) 2015-08-14 2017-02-23 Gradiant Corporation Selective retention of multivalent ions
WO2017030937A1 (en) 2015-08-14 2017-02-23 Gradiant Corporation Production of multivalent ion-rich process streams using multi-stage osmotic separation
WO2017030941A1 (en) 2015-08-14 2017-02-23 Gradiant Corporation Production of multivalent ion-rich streams using humidification-dehumidification systems
WO2017044645A1 (en) 2015-09-08 2017-03-16 Gradiant Corporation Systems and methods for treatment of water, such as oilfield wastewater, via chemical coagulation
WO2017044668A1 (en) 2015-09-08 2017-03-16 Gradiant Corporation Systems and methods for removal of boron from water, such as oilfield wastewater
WO2017127607A1 (en) 2016-01-22 2017-07-27 Gradiant Corporation Formation of solid salts using high gas flow velocities in humidifiers, such as multi-stage bubble column humidifiers
WO2017147113A1 (en) 2016-02-22 2017-08-31 Gradiant Corporation Hybrid desalination systems and associated methods
US20180008919A1 (en) 2016-07-06 2018-01-11 Gradiant Corporation Solids handling in water treatment systems and associated methods
JP2018001111A (en) 2016-07-05 2018-01-11 東洋紡株式会社 Processing method of desalinating salt water and processing system of desalinating salt water
US20180036682A1 (en) 2015-03-05 2018-02-08 Surrey Aquatechnology Limited Purification of highly saline feeds
US20180104649A1 (en) 2016-10-19 2018-04-19 Gradiant Corporation Osmotic Membrane
US9950297B2 (en) 2013-02-06 2018-04-24 Korea Advanced Institute Of Science And Technology Method for concentrating aqueous containing solute into high concentration by hydraulic-membrane process under no difference in osmotic pressure
WO2018084246A1 (en) 2016-11-02 2018-05-11 東洋紡株式会社 Concentration method and concentration device
US10258926B2 (en) 2015-02-11 2019-04-16 Massachusetts Institute Of Technology Hybridization of humidification-dehumidification and pressure-retarded osmosis
WO2019097261A1 (en) 2017-11-20 2019-05-23 Surrey Aquatechnology Limited Solvent separation
US10308524B1 (en) 2019-01-15 2019-06-04 Kuwait Institute For Scientific Research Pressure-reduced saline water treatment system
US20190224624A1 (en) 2017-02-15 2019-07-25 Hitachi, Ltd. Reverse osmosis treatment apparatus and reverse osmosis treatment method
US10940439B1 (en) 2019-12-10 2021-03-09 Kuwait Institute For Scientific Research High water recovery hybrid membrane system for desalination and brine concentration
US10953367B2 (en) 2015-07-24 2021-03-23 Lab to Market Inc. Method of osmotic pressure free reverse osmosis for enriching solute-containing solution to high concentration

Patent Citations (447)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US2151990A (en) 1938-02-19 1939-03-28 Shell Dev Recovery of organic compounds
US2606820A (en) 1947-09-25 1952-08-12 Dorr Co Apparatus for precipitation of solids from solutions and the like
US2640018A (en) 1949-07-25 1953-05-26 Signal Oil & Gas Co Method of steam distillation
US2606839A (en) 1951-03-21 1952-08-12 Dow Chemical Co Noncaking sea salt and method of producing the same
GB821939A (en) 1954-12-23 1959-10-14 Gerolamo Nossardi Method of and installation for the continuous extraction of magnesium with milk of lime from sea waters and the like
US3080302A (en) 1958-11-04 1963-03-05 Submerged Comb Inc Process and apparatus for converting non-potable water to potable water
US2997856A (en) 1959-03-06 1961-08-29 John W Pike Method and apparatus for producing fresh water from saline water
US3032482A (en) 1959-04-02 1962-05-01 Richard W Shoemaker Process of recovering fresh water from salt water with a hot heavy material
US3042606A (en) 1960-05-31 1962-07-03 Grace W R & Co Descaling sea water
US3236747A (en) 1962-02-21 1966-02-22 Halcon International Inc Process for separating volatile material from a liquid mixture by a series of vaporization stages
GB1013767A (en) 1962-04-18 1965-12-22 Aqua Chem Inc Method and apparatus for purifying liquids
GB1036920A (en) 1963-12-20 1966-07-20 Norris Bros Ltd Improvements in or relating to the production of potable water from sea water
US3489652A (en) 1966-04-18 1970-01-13 American Mach & Foundry Desalination process by multi-effect,multi-stage flash distillation combined with power generation
US3331773A (en) 1966-07-22 1967-07-18 Grace W R & Co Process for inhibiting precipitation in water
US3454490A (en) 1966-08-10 1969-07-08 Atomic Energy Commission Concentration of ions using ion selective membranes
US3472766A (en) 1968-01-10 1969-10-14 Dow Chemical Co Separatory process utilizing a permeable polyamide membrane having poly (oxyethylene) grafts
US3475331A (en) 1968-02-23 1969-10-28 Dow Chemical Co Permeability separatory apparatus and process of making and using same
US3630378A (en) 1968-05-24 1971-12-28 Dow Chemical Co Novel water treating and storage apparatus
FR1582201A (en) 1968-07-24 1969-09-26
US3625761A (en) 1969-12-23 1971-12-07 Texaco Inc Method for the treatment of alkaline earth metal sulfate scale
US3725209A (en) 1970-08-11 1973-04-03 F Rosa Centrifugal distillation system
GB1320429A (en) 1970-12-10 1973-06-13 Israel Prime Ministers Office Process and apparatus for reverse osmosis
DE2145861C2 (en) 1971-09-14 1973-06-07 Preussag Ag, 3000 Hannover Process and device for the preparation of recent colorful and precious metal-containing sea sludge by leaching using chlorine gas and metal clones
GB1444241A (en) 1972-08-08 1976-07-28 Tabata H Preparation of freshwater from sea water
US3922154A (en) 1972-09-11 1975-11-25 Agency Ind Science Techn Method for purification of sodium hydroxide
US3906250A (en) 1973-07-03 1975-09-16 Univ Ben Gurion Method and apparatus for generating power utilizing pressure-retarded-osmosis
US4156645A (en) 1973-07-26 1979-05-29 Desalination Systems Inc. Conversion of sea water by reverse osmosis
US3926739A (en) 1973-08-15 1975-12-16 Hitachi Ltd Multiple-effect multi-stage flash evaporation process and apparatus for demineralizing water
US4105547A (en) 1974-12-23 1978-08-08 Alfa-Laval Ab Filtering process
US4224148A (en) 1975-07-18 1980-09-23 Lindman William E Galvanic flow system for joint particulate recovery and liquid purification
US4062197A (en) 1976-07-09 1977-12-13 Hester Jarrett C Absorption heating-cooling system
US4334886A (en) 1978-02-24 1982-06-15 Katsuhiko Tani Method of manufacturing table salt
US4251367A (en) 1979-01-25 1981-02-17 Waste Conversion Technology, Inc. Wastewater treatment
JPS55147199A (en) 1979-05-07 1980-11-15 Shigeo Maekawa Recovering method for fresh water and solid matter from seawater containing mud or muddy water
US4312755A (en) 1979-06-29 1982-01-26 Dow Corning Corporation Reverse osmosis system
US4478719A (en) 1979-11-22 1984-10-23 Helmut Michele Method and apparatus for the separation of fluids by permeation
US4358377A (en) 1980-09-02 1982-11-09 The Dow Chemical Company Shear-vectoring design for composite casing end and removable, pressure-locking closure therefor
US4452696A (en) 1981-04-06 1984-06-05 Fernand Lopez Reverse-osmosis apparatus for producing fresh water from seawater
US4576724A (en) 1981-06-25 1986-03-18 Colman Derek A Cyclone separator
EP0070059A1 (en) 1981-07-10 1983-01-19 Nederlandse Organisatie voor toegepast-natuurwetenschappelijk onderzoek TNO Method and apparatus for concentrating solutions by means of reverse osmosis
US4511436A (en) 1982-05-24 1985-04-16 D.V.T. Buro Fur Anwendung Deutscher Verfahrenstechnik H. Morsy Apparatus for the desalination of sea water
US4563337A (en) 1982-08-13 1986-01-07 General Electric Company Method and apparatus for continuous ion exchange
FR2561637A1 (en) 1984-03-20 1985-09-27 Guiffray Michel Process and device for producing distilled water from seawater
US4574049A (en) 1984-06-04 1986-03-04 Arrowhead Industrial Water, Inc. Reverse osmosis system
US4574049B1 (en) 1984-06-04 1999-02-02 Ionpure Filter Us Inc Reverse osmosis system
JPH06233B2 (en) 1984-06-04 1994-01-05 アローヘツド、インダストリアル、ウオーター、インコーポレイテツド Reverse osmosis water purification method
US4941972A (en) 1984-12-06 1990-07-17 The Dow Chemical Company Chlorine-stable membrane compositions
US4839203A (en) 1985-04-03 1989-06-13 The Dow Chemical Company Semi-permeable membranes prepared via reaction of cationic groups with nucleophilic groups
US4704324A (en) 1985-04-03 1987-11-03 The Dow Chemical Company Semi-permeable membranes prepared via reaction of cationic groups with nucleophilic groups
EP0207390A1 (en) 1985-06-22 1987-01-07 BASF Aktiengesellschaft Process for the recovery of amine and metal compounds in the preparation of polyphenylene ether
US4843828A (en) 1985-10-04 1989-07-04 The Boc Group, Plc Liquid-vapor contact method and apparatus
US4770775A (en) 1985-10-10 1988-09-13 Fernand Lopez Apparatus for the production of fresh water from sea water by reverse osmosis
US4797187A (en) 1985-10-22 1989-01-10 The Dow Chemical Company Semi-permeable membranes prepared via reaction of cationic groups with nucleophilic groups
US5053132A (en) 1985-10-22 1991-10-01 The Trustees Of The Stevens Institute Of Technology Asymmetrically-wettable porous membrane
US4652373A (en) 1986-02-21 1987-03-24 The Dow Chemical Company Tubesheet for spiral wound hollow fiber permeator
US4765897A (en) 1986-04-28 1988-08-23 The Dow Chemical Company Polyamide membranes useful for water softening
US4824574A (en) 1986-04-28 1989-04-25 The Dow Chemical Company Novel water softening process using membranes
US5123481A (en) 1986-07-09 1992-06-23 Walter F. Albers Method and apparatus for simultaneous heat and mass transfer
US4832115A (en) 1986-07-09 1989-05-23 Albers Technologies Corporation Method and apparatus for simultaneous heat and mass transfer
EP0253287A1 (en) 1986-07-15 1988-01-20 The Dow Chemical Company Combined membrane and sorption process for selective ion removal
US4806244A (en) 1986-07-15 1989-02-21 The Dow Chemical Company Combined membrane and sorption process for selective ion removal
US4927540A (en) 1986-09-04 1990-05-22 The Dow Chemical Company Ionic complex for enhancing performance of water treatment membranes
US4981593A (en) 1986-09-16 1991-01-01 Commonwealth Scientific And Industrial Research Organisation Sewage treatment
US4708805A (en) 1986-11-24 1987-11-24 Muhala Thomas F D Barium sulfate removal and anti-deposition compositions and process of use therefor
US4755298A (en) 1986-12-04 1988-07-05 The Dow Chemical Company Process for removing boron ions from aqueous solutions
US4812238A (en) 1987-01-15 1989-03-14 The Dow Chemical Company Membranes prepared via reaction of diazonium compounds or precursors
US4735722A (en) 1987-06-15 1988-04-05 Krepak John C Desalination of seawater or brackish water
US4894165A (en) 1987-07-20 1990-01-16 The Dow Chemical Company Rejection enhancing coatings for reverse osmosis membranes
US4909943A (en) 1987-07-20 1990-03-20 The Dow Chemical Company Rejection enhancing coatings for reverse osmosis membranes
US4828700A (en) 1987-07-20 1989-05-09 The Dow Chemical Company Rejection enhancing coatings for reverse osmosis membranes
US4859338A (en) 1987-08-06 1989-08-22 Thyssen Edelstahlwerke Ag Filter for small particles
US4859384A (en) 1987-11-18 1989-08-22 Filmtec Corp. Novel polyamide reverse osmosis membranes
US4769148A (en) 1987-11-18 1988-09-06 The Dow Chemical Company Novel polyamide reverse osmosis membranes
US4992485A (en) 1988-10-11 1991-02-12 The Dow Chemical Company Microporous peek membranes and the preparation thereof
US4957817A (en) 1988-11-25 1990-09-18 The Dow Chemical Film, fiber, and microporous membranes of poly(etheretherketone)dissolved in high boiling point polar organic solvents
US4980063A (en) 1989-01-27 1990-12-25 The Dow Chemical Company Compositions useful for preparing cellulose ester membranes for liquid separations
US4956157A (en) 1989-02-20 1990-09-11 Atsushi Nasu Process for separating salts in seawater
US5282995A (en) 1989-04-03 1994-02-01 Mobil Oil Corporation Composition for removing an alkaline earth metal sulfate scale
US5190656A (en) 1989-04-03 1993-03-02 Mobil Oil Corporation Method for removing scale via a liquid membrane in combination with an amino carboxylic acid and a catalyst
US4944882A (en) 1989-04-21 1990-07-31 Bend Research, Inc. Hybrid membrane separation systems
US4959237A (en) 1989-06-07 1990-09-25 E. I. Du Pont De Nemours And Company Reverse osmosis concentration of juice products with improved flavor
US5096590A (en) 1989-06-19 1992-03-17 Director Of National Food Research Institute, Ministry Of Agriculture, Forestry And Fisheries Concentration of solution by the reverse osmosis process
US4980077A (en) 1989-06-22 1990-12-25 Mobil Oil Corporation Method for removing alkaline sulfate scale
US5015391A (en) 1989-12-12 1991-05-14 Betz Laboratories, Inc. Silicate coagulant aid for treatment of oily wastewaters
US4973201A (en) 1990-03-09 1990-11-27 Mobil Oil Corporation Method for removing scale and radioactive material from earth
US5238574A (en) 1990-06-25 1993-08-24 Kawasaki Jukogyo Kabushiki Kaisha Method and apparatus having reverse osmosis membrane for concentrating solution
US5490937A (en) 1990-09-17 1996-02-13 Genentech, Inc. Tangential flow filtration process and apparatus
US5225087A (en) 1991-05-10 1993-07-06 Westinghouse Electric Corp. Recovery of EDTA from steam generator cleaning solutions
US5453205A (en) 1991-05-29 1995-09-26 Modern Environmental Service Trust Treatment of emulsions
JPH05208199A (en) 1991-10-07 1993-08-20 Nalco Chem Co Method for controlling scale in device for usein stratum containing petruleum and in relation thereto
US5167828A (en) 1991-10-07 1992-12-01 Nalco Chemical Company Phosphinate-containing polymers for controlling scale in underground petroleum-containing formations and equipment associated therewith
US5250185A (en) 1992-05-01 1993-10-05 Texaco Inc. Reducing aqueous boron concentrations with reverse osmosis membranes operating at a high pH
US5207916A (en) 1992-05-20 1993-05-04 Mesco, Inc. Reverse osmosis system
US5328616A (en) 1992-11-20 1994-07-12 Monsanto Company Methods and apparatus for treating electroless plating baths
EP0623561A1 (en) 1993-04-05 1994-11-09 Electricite De France Process and device for decontaminating a liquid effluent containing ionic metals
US5656161A (en) 1993-04-20 1997-08-12 Ionics, Incorporated Salt basket for crystallizer and method of use in zero liquid discharge industrial facilities
US5503750A (en) 1993-10-04 1996-04-02 Russo, Jr.; Lawrence J. Membrane-based process for the recovery of lactic acid by fermentation of carbohydrate substrates containing sugars
US5425902A (en) 1993-11-04 1995-06-20 Tom Miller, Inc. Method for humidifying air
US5464540A (en) 1993-12-09 1995-11-07 Bend Research, Inc. Pervaporation by countercurrent condensable sweep
WO1995027683A1 (en) 1994-04-06 1995-10-19 Zenon Environmental, Inc. Microfiltration enhanced reverse osmosis for water treatment
US6010631A (en) 1994-05-02 2000-01-04 Omnium De Traitement Et De Valorisation (Otv) Method and installation for treating an untreated flow by simple sedimentation after ballasting with fine sand
US6187200B1 (en) 1994-10-12 2001-02-13 Toray Industries, Inc. Apparatus and method for multistage reverse osmosis separation
US5840195A (en) 1995-05-01 1998-11-24 Omnium De Traitement Et De Valorisation Method and installation for treating an untreated flow by simple sedimentation after ballasting with fine sand
US5670053A (en) 1995-08-07 1997-09-23 Zenon Environmental, Inc. Purification of gases from water using reverse osmosis
US20030178367A1 (en) 1996-01-17 2003-09-25 Van Reis Robert D. Tangential-flow filtration system
US20020108907A1 (en) 1996-01-17 2002-08-15 Van Reis Robert D. Tangential-flow filtration system
US20110094965A1 (en) 1996-10-01 2011-04-28 Riad Al-Samadi Enhanced High Water Recovery Membrane Process
US6113797A (en) 1996-10-01 2000-09-05 Al-Samadi; Riad A. High water recovery membrane purification process
US6461514B1 (en) 1996-10-01 2002-10-08 Riad A. Al-Samadi High water recovery single stage membrane process
US6062070A (en) 1996-10-29 2000-05-16 Drexelbrook Controls, Inc. Method and apparatus for the sonic measurement of sludge and clarity conditions during the treatment of waste water
US5873260A (en) 1997-04-02 1999-02-23 Linhardt; Hans D. Refrigeration apparatus and method
US6508936B1 (en) 1997-10-01 2003-01-21 Saline Water Conversion Corporation Process for desalination of saline water, especially water, having increased product yield and quality
US6146525A (en) 1998-02-09 2000-11-14 Cycteck Environmental, Inc. Apparatus and methods for separating particulates from a particulate suspension in wastewater processing and cleaning
US6547965B1 (en) 1998-02-27 2003-04-15 Nate International Large tube assemblies for reverse osmosis
WO2000000273A1 (en) 1998-06-29 2000-01-06 Hw Process Technologies, Inc. Method of removing sulfate and/or metal ions from waters or wastewaters
US6056878A (en) 1998-08-03 2000-05-02 E-Cell Corporation Method and apparatus for reducing scaling in electrodeionization systems and for improving efficiency thereof
US6319409B1 (en) 1998-09-11 2001-11-20 Fuji Jukogyo Kabushiki Kaisha Process for treating waste water containing cutting oil
US6190556B1 (en) 1998-10-12 2001-02-20 Robert A. Uhlinger Desalination method and apparatus utilizing nanofiltration and reverse osmosis membranes
US6440310B1 (en) 1999-01-08 2002-08-27 United States Filter Corporation Method and apparatus for microfiltration
US6270671B1 (en) 1999-01-08 2001-08-07 United States Filter Corporation Method and apparatus for microfiltration
US6190558B1 (en) 1999-04-01 2001-02-20 Nimbus Water Systems, Inc. Reverse osmosis purification system
US6423235B1 (en) 1999-08-18 2002-07-23 Nittetu Chemical Engineering Ltd. Column gas-liquid contacting apparatus and its use thereof
WO2001014256A1 (en) 1999-08-20 2001-03-01 L.E.T. Leading Edge Technologies Limited A salt water desalination process using ion selective membranes
US6783682B1 (en) 1999-08-20 2004-08-31 L.E.T., Leading Edge Technologies Limited Salt water desalination process using ion selective membranes
US6416668B1 (en) 1999-09-01 2002-07-09 Riad A. Al-Samadi Water treatment process for membranes
JP2002001068A (en) 2000-06-21 2002-01-08 Kurita Water Ind Ltd Method and apparatus for membrane separation
US6299766B1 (en) 2000-07-06 2001-10-09 Clark Permar Reverse osmosis filtering apparatus with concentrate dilution
US6582605B2 (en) 2000-07-07 2003-06-24 Ionics, Incorporated Method of treating industrial waste waters
WO2002032813A1 (en) 2000-10-21 2002-04-25 Pb Power Ltd. Process and plant for multi-stage flash desalination of water
US20060127550A1 (en) 2001-01-16 2006-06-15 Kagome Kabushiki Kaisha Apparatus for concentrating processed vegetable and fruit products by reverse osmosis
US7465376B2 (en) 2001-02-22 2008-12-16 Susanne Neubert Method and device for treating liquids
US6730234B2 (en) 2001-03-15 2004-05-04 Tetra Technologies, Inc. Method for regeneration of used halide fluids
US7115670B2 (en) 2001-05-25 2006-10-03 Bp Exploration Operating Company Limited Fischer-Tropsch synthesis process
US7459084B2 (en) 2001-06-22 2008-12-02 Petro Sep International Ltd. Membrane-assisted fluid separation apparatus and method
US6699369B1 (en) 2001-08-10 2004-03-02 Aquasonics International Apparatus and method for thermal desalination based on pressurized formation and evaporation of droplets
US20030106860A1 (en) 2001-11-09 2003-06-12 Guy Peloquin Apparatus for and method of settling of mineral slurries
US20030132166A1 (en) 2002-01-15 2003-07-17 Paul Rey Method of treating mine drainage
US8366924B2 (en) 2002-05-02 2013-02-05 City Of Long Beach Two stage nanofiltration seawater desalination system
US20070080113A1 (en) 2002-05-02 2007-04-12 City Of Long Beach Two stage nanofiltration seawater desalination system
US7048852B2 (en) 2002-10-31 2006-05-23 Infilco Degremont, Inc. Method and apparatus for treating water or wastewater to reduce organic and hardness contamination
US7597784B2 (en) 2002-11-13 2009-10-06 Deka Products Limited Partnership Pressurized vapor cycle liquid distillation
GB2395946A (en) 2002-12-05 2004-06-09 Thomas Altmann Extracting sodium chloride from seawater, using nanofiltration
US6919000B2 (en) 2002-12-17 2005-07-19 University Of Florida Diffusion driven desalination apparatus and process
US7225620B2 (en) 2002-12-17 2007-06-05 University Of Florida Research Foundation, Inc. Diffusion driven water purification apparatus and process
US20040187897A1 (en) 2002-12-18 2004-09-30 Andy Kenowski Monitoring device and method for operating clean-in-place system
US7022240B2 (en) 2003-01-15 2006-04-04 Hart Resource Technologies, Inc. Method for on-site treatment of oil and gas well waste fluids
US6817476B2 (en) 2003-01-31 2004-11-16 Aerex Industries, Inc. Water clarification system
US20060150892A1 (en) 2003-04-29 2006-07-13 Akzo Nobel N.V. Processes Involving the Use of Antisolvent Crystallisation
US20050023222A1 (en) 2003-05-30 2005-02-03 Brian Baillie Filtration apparatus and method
CN1856447A (en) 2003-07-30 2006-11-01 萨里大学 Solvent removal process
US20110114558A1 (en) 2003-07-30 2011-05-19 Abdulsalam Al-Mayahi Solvent Removal Process
WO2005012185A1 (en) 2003-07-30 2005-02-10 University Of Surrey Solvent removal process
CN1835892A (en) 2003-08-17 2006-09-20 艾维·艾弗雷提 Continuous closed-circuit desalination apparatus with single container
US7628921B2 (en) 2003-08-17 2009-12-08 Avi Efraty Apparatus for continuous closed circuit desalination under variable pressure with a single container
US20070012556A1 (en) 2003-12-02 2007-01-18 Lum Gary W Water processing apparatus
US20070068791A1 (en) 2003-12-02 2007-03-29 Thom Douglas M Automated water processing control system
US20080116134A1 (en) 2004-01-30 2008-05-22 Cartwright Peter S Brine-Conserving Nanofiltration Water Softener System
US20080237110A1 (en) 2004-05-21 2008-10-02 Wisconsin Alumni Research Foundation Membrane cascade-based separation
US8152999B2 (en) 2004-05-21 2012-04-10 Wisconsin Alumni Research Foundation Membrane cascade-based separation
US7141171B2 (en) 2004-05-21 2006-11-28 Wisconsin Alumni Research Foundation Membrane cascade-based separation
US7316080B1 (en) 2004-05-27 2008-01-08 Solution Dynamics, Llc Methodology and apparatus to reduce fuel consumption in conveyor dryers and ovens
US7306437B2 (en) 2004-08-10 2007-12-11 Leif Hauge Pressure exchanger
CN101056693A (en) 2004-09-13 2007-10-17 南卡罗来纳大学 Water desalination process and apparatus
US7459088B2 (en) 2004-09-13 2008-12-02 The University Of South Carolina Water desalination process and apparatus
CN1623936A (en) 2004-10-26 2005-06-08 南京工业大学 Technology for recovering ash water of coal-fired power plant and system of sealing circulating for recovering thereof
US20110233137A1 (en) 2004-12-06 2011-09-29 Cath Tzahi Y Systems and methods for purification of liquids
US20060144787A1 (en) 2005-01-06 2006-07-06 Eet Corporation Integrated electro-pressure membrane deionization system
US20060157409A1 (en) 2005-01-14 2006-07-20 Saline Water Conversion Corporation (Swcc) Optimal high recovery, energy efficient dual fully integrated nanofiltration seawater reverse osmosis desalination process and equipment
US20060157410A1 (en) 2005-01-14 2006-07-20 Saline Water Conversion Corporation (Swcc) Fully integrated NF-thermal seawater desalination process and equipment
US20070102359A1 (en) 2005-04-27 2007-05-10 Lombardi John A Treating produced waters
US20090020289A1 (en) 2005-05-06 2009-01-22 University Of Surrey Secondary oil recovery
US7726398B2 (en) 2005-06-16 2010-06-01 Bp Exploration Operating Company Limited Water flooding method
EP1775267A2 (en) 2005-06-23 2007-04-18 Esposito Servizi Ecologici s.r.l. Plant and process for the recycling of sweepings, water purifier wastes and the like
US8043509B2 (en) 2005-07-06 2011-10-25 Sylvan Source, Inc. Water purification system
US20090101490A1 (en) 2005-07-06 2009-04-23 Sylvan Source, Inc. Water Purification System
US7727400B2 (en) 2005-09-23 2010-06-01 Michael Flynn Low water recovery rate desalination system and method
US20090218210A1 (en) 2005-10-14 2009-09-03 Laura Demmons Energy-efficient distillation system
US20070084713A1 (en) 2005-10-19 2007-04-19 Deep Richard J Water purification system
US7678235B2 (en) 2005-10-19 2010-03-16 Sylvan Source, Inc. Water purification system
US20070131428A1 (en) 2005-10-24 2007-06-14 Willem Cornelis Den Boestert J Methods of filtering a liquid stream produced from an in situ heat treatment process
US7964101B2 (en) 2006-01-25 2011-06-21 Q'max Solutions Inc. Fluid treatment process
US7527726B2 (en) 2006-01-25 2009-05-05 Q'max Solutions Inc. Fluid treatment apparatus
US20070181480A1 (en) 2006-02-09 2007-08-09 Dong-Won Lee Water filtering device
US20090308820A1 (en) 2006-03-03 2009-12-17 Eugene Thiers Contaminant Prevention
US8562824B2 (en) 2006-03-03 2013-10-22 Sylvan Source, Inc. Contaminant prevention
US8794320B2 (en) 2006-03-27 2014-08-05 Shell Oil Company Water injection systems and methods
US20070246406A1 (en) 2006-03-31 2007-10-25 Dibel Kevin R Tangential flow filtration apparatuses, systems, and processes for the separation of compounds
US20070235391A1 (en) 2006-04-11 2007-10-11 Sorbwater Technology As Method for removal of materials from a liquid stream
WO2007128062A1 (en) 2006-05-05 2007-11-15 Newcastle Innovation Limited Desalination method and apparatus
WO2007132477A1 (en) 2006-05-11 2007-11-22 Raman Ahilan A pretreatment process for the saline water feeds of desalination plants
CN100999364A (en) 2006-05-16 2007-07-18 葛文宇 Comprehensive utilization high advantage zero discharge seawater desalination production technology
WO2007138327A1 (en) 2006-06-01 2007-12-06 Natco Uk Limited Method of providing a supply of water of controlled salinity and water treatment system
US20090194272A1 (en) 2006-06-14 2009-08-06 Vws Westgarth Limited Apparatus and method for treating injection fluid
WO2007144591A1 (en) 2006-06-14 2007-12-21 Vws Westgarth Limited Apparatus and method for treating injection fluid
US20080023333A1 (en) 2006-07-17 2008-01-31 Brendan Johnson Microscale capacitive deionization apparatus
US20100234795A1 (en) 2006-08-16 2010-09-16 Wallenaes Anders System and method for regeneration of a fluid
US7510656B2 (en) 2006-09-01 2009-03-31 Anticline Disposal, Llc Waste water treatment method
US8147696B1 (en) 2006-09-19 2012-04-03 Pandya Ken V High-efficiency water-softening process
US20080073200A1 (en) 2006-09-22 2008-03-27 Altela, Inc. Novel enhanced systems, processes and methodologies for producing clean water and products thereby
US20120199534A1 (en) 2006-10-10 2012-08-09 Terrabon Adve, Llc Desalination methods
CN101636354A (en) 2006-10-10 2010-01-27 得克萨斯A&M大学系统 Desalination system
US20130092626A1 (en) 2006-10-30 2013-04-18 Perlemax Ltd Bubble generation for aeration and other purposes
US20080102119A1 (en) 2006-11-01 2008-05-01 Medtronic, Inc. Osmotic pump apparatus and associated methods
US20080121585A1 (en) 2006-11-27 2008-05-29 Mavis James D Water treatment using de-supersaturation
US7815804B2 (en) 2006-12-12 2010-10-19 Otv Sa S.A. Method for treating wastewater or produced water
US20080164206A1 (en) 2007-01-10 2008-07-10 Southwest Turf Solutions, Inc. Method and apparatus for removing minerals from a water source
US20100163472A1 (en) 2007-03-21 2010-07-01 Sylvan Source, Inc. Water purification system
US20080245737A1 (en) 2007-04-03 2008-10-09 Siemens Water Technologies Corp. Method and system for providing ultrapure water
WO2008137082A1 (en) 2007-05-02 2008-11-13 Yale University Method for designing membranes for osmotically driven membrane processes
US20080277344A1 (en) 2007-05-11 2008-11-13 Arup K. Sengupta Brackish and sea water desalination using a hybrid ion exchange-nanofiltration process
US7731847B2 (en) 2007-05-25 2010-06-08 Huy Ton That Submersible reverse osmosis desalination apparatus and method
US20100294718A1 (en) 2007-06-08 2010-11-25 Swiss Fresh Water Sa Liquid purification system using a medium pressure membrane
US8678080B2 (en) 2007-07-19 2014-03-25 Shell Oil Company Water processing systems and methods
US8469092B2 (en) 2007-07-19 2013-06-25 Shell Oil Company Water processing system and methods
US7950921B1 (en) 2007-07-20 2011-05-31 Solution Dynamics, Llc Method and apparatus for cooling the underside of kiln cars
US20090032446A1 (en) 2007-08-01 2009-02-05 Triwatech, L.L.C. Mobile station and methods for diagnosing and modeling site specific effluent treatment facility requirements
US20110257788A1 (en) 2007-08-01 2011-10-20 Wiemers Reginald A Mobile station and methods for diagnosing and modeling site specific full-scale effluent treatment facility requirements
US7824552B2 (en) 2007-09-05 2010-11-02 Halliburton Energy Services, Inc. Mobile systems and methods of sufficiently treating water so that the treated water may be utilized in well-treatment operations
US8012358B2 (en) 2007-09-05 2011-09-06 Halliburton Energy Services, Inc. Mobile systems and methods of sufficiently treating water so that the treated water may be utilized in well-treatment operations
CN101397152A (en) 2007-09-28 2009-04-01 旭化成化学株式会社 Brine treatment method
US20090101587A1 (en) 2007-10-22 2009-04-23 Peter Blokker Method of inhibiting scale formation and deposition in desalination systems
US20090127210A1 (en) 2007-11-20 2009-05-21 Swisher Anthony E Method and apparatus for water remediation
US7718069B2 (en) 2007-12-06 2010-05-18 Water & Power Technologies, Inc. Water treatment process for oilfield produced water
US7520993B1 (en) 2007-12-06 2009-04-21 Water & Power Technologies, Inc. Water treatment process for oilfield produced water
US20090173690A1 (en) 2008-01-04 2009-07-09 Fluid Equipment Development Company, Llc Batch-operated reverse osmosis system
US20090173096A1 (en) 2008-01-08 2009-07-09 Calvin Wade Wohlert Methodology for converting existing packaged rooftop air conditioning units to be served from a centralized water cooled refrigeration and/or heat pump system
US20090277641A1 (en) 2008-05-07 2009-11-12 Harold Walters Methods of using a lower-quality water for use as some of the water in the forming and delivering of a treatment fluid into a wellbore
US20090277640A1 (en) 2008-05-07 2009-11-12 Jonn Thompson Methods of using a higher-quality water with an unhydrated hydratable additive allowing the use of a lower-quality water as some of the water in the forming and delivering of a treatment fluid into a wellbore
US20090277634A1 (en) 2008-05-07 2009-11-12 Leonard Case Methods of pumping fluids having different concentrations of particulate with different concentrations of hydratable additive to reduce pump wear and maintenance in the forming and delivering of a treatment fluid into a wellbore
US20150136699A1 (en) 2008-06-13 2015-05-21 Solution Dynamics, Llc Apparatus and methods for solution processing
US20120273422A1 (en) 2008-06-13 2012-11-01 Calvin Wade Wohlert Apparatus and methods for solution processing using reverse osmosis
US20180169583A1 (en) 2008-06-13 2018-06-21 Solution Dynamics, Llc Apparatus and methods for solution processing
US9751045B2 (en) 2008-06-13 2017-09-05 Solution Dynamics, Llc Apparatus and methods for solution processing
US8216473B2 (en) 2008-06-13 2012-07-10 Solution Dynamics, Llc Apparatus and methods for solution processing using reverse osmosis
US20190176088A1 (en) 2008-06-13 2019-06-13 Solution Dynamics, Llc Apparatus and methods for solution processing
US20100032377A1 (en) 2008-06-13 2010-02-11 Calvin Wade Wohlert Apparatus and methods for solution processing using reverse osmosis
US8840792B2 (en) 2008-06-13 2014-09-23 Solution Dynamics, Inc. Apparatus and methods for solution processing using reverse osmosis
US20110108484A1 (en) 2008-07-09 2011-05-12 I.D.E. Technologies Ltd. Method of improving performance of a reverse osmosis system for seawater desalination, and modified reverse osmosis system obtained thereby
CN102143786A (en) 2008-09-04 2011-08-03 I·D·E·技术有限公司 Improved water desalination system
WO2010026589A1 (en) 2008-09-04 2010-03-11 I.D.E. Technologies Ltd. Improved water desalination system
US9550685B2 (en) 2008-09-04 2017-01-24 University Of Florida Research Foundation, Inc. Desalination apparatus and process
US8771477B2 (en) 2008-09-17 2014-07-08 Sylvan Source, Inc. Large-scale water purification and desalination
US20140299462A1 (en) 2008-09-17 2014-10-09 Sylvan Source, Inc. Large-scale water purification and desalination
US20140246368A1 (en) 2008-11-11 2014-09-04 P & Ls Holding Gmbh Membrane separation devices and water treatment plants
CN101417208A (en) 2008-11-14 2009-04-29 清华大学 Extractive agent recovering method in water phase using film isolation technique
US20110203929A1 (en) 2008-11-17 2011-08-25 David Buckley Recovery of lithium from aqueous solutions
CN102036739A (en) 2008-11-17 2011-04-27 凯米涛弗特公司 Recovery of lithium from aqueous solutions
US20100132386A1 (en) 2008-12-02 2010-06-03 Xergy Incorporated Electrochemical Compressor and Refrigeration System
US20140061022A1 (en) 2008-12-15 2014-03-06 Water Desalination International, Inc. Water Desalination System
US20100163471A1 (en) 2008-12-30 2010-07-01 Irving Elyanow Water desalination plant and system for the production of pure water and salt
US20110306525A1 (en) 2009-02-13 2011-12-15 Dirk Jacob Lighthelm Aqueous displacement fluid injection for enhancing oil recovery from an oil bearing formation
US20100242995A1 (en) 2009-03-26 2010-09-30 General Electric Company Method for removing ionic species from desalination unit
CN102725236A (en) 2009-04-10 2012-10-10 纯净源公司 Method and system for reduction of scaling in purification of aqueous solutions
WO2010118425A1 (en) 2009-04-10 2010-10-14 Sylvan Source, Inc. Method and system for reduction of scaling in purification of aqueous solutions
US20120125861A1 (en) 2009-04-10 2012-05-24 Sylvan Source, Inc. Method and system for reduction of scaling in purification of aqueous solutions
WO2010122336A2 (en) 2009-04-21 2010-10-28 Abdulsalam Al-Mayahi Water treatment
US20100282675A1 (en) 2009-05-08 2010-11-11 Lehigh University System and method for reversible cation-exchange desalination
WO2010131251A2 (en) 2009-05-13 2010-11-18 Renewed Water Minerals Ltd. Separation of mg2+ ions from sea-and brackish water for the purpose of re-mineralization of water and wastewater
CN102438957A (en) 2009-05-20 2012-05-02 水技术国际公司 Method for treatment and purification of seawater to recover high purity sodium chloride for industrial usage
WO2010135561A2 (en) 2009-05-20 2010-11-25 Aquatech International Corporation Method for treatment and purification of seawater to recover high purity sodium chloride for industrial usage
US20110017677A1 (en) 2009-06-04 2011-01-27 Evans Thomas S Oil field water recycling system and method
US20120125611A1 (en) 2009-06-25 2012-05-24 Shell Internationalale Research Maatschappij Water injection systems and methods
US20110024354A1 (en) 2009-07-30 2011-02-03 General Electric Company Desalination system and method
US8292272B2 (en) 2009-09-04 2012-10-23 Massachusetts Institute Of Technology Water separation under reduced pressure
US20110056822A1 (en) 2009-09-04 2011-03-10 Massachusetts Institute Of Technology Water Separation Under Reduced Pressure
US20110056878A1 (en) 2009-09-10 2011-03-10 Takeshi Matsushiro Membrane filtration system
US8252092B2 (en) 2009-10-05 2012-08-28 Massachusetts Institute Of Technology Water separation under varied pressure
US20120205307A1 (en) 2009-10-27 2012-08-16 Vws Westgarth Limited Fluid treatment apparatus and method
US20120273417A1 (en) 2009-10-28 2012-11-01 Oasys Water, Inc. Forward osmosis separation processes
US20120234664A1 (en) 2009-10-28 2012-09-20 Surrey Aquatechnology Ltd. Thermal Desalination
US20120067819A1 (en) 2009-10-28 2012-03-22 Oasys Water, Inc. Osmotically driven membrane processes and systems and methods for draw solute recovery
CN101717161A (en) 2009-10-30 2010-06-02 葛文宇 Production process for achieving hundred-percent comprehensive utilization and zero emission by recycling and extracting seawater
US20110120157A1 (en) 2009-10-30 2011-05-26 Calvin Wohlert Absorption refrigeration cycles; apparatus; and, methods
US20120227975A1 (en) 2009-11-02 2012-09-13 Ayirala Subhash Chandra Bose Water injection systems and methods
US8119007B2 (en) 2009-11-25 2012-02-21 Massachusetts Institute Of Technology Water desalination using directional solvent extraction
US20120285886A1 (en) 2009-11-25 2012-11-15 I.D.E. Technologies Ltd. Reciprocal enhancement of reverse osmosis and forward osmosis
US8501007B2 (en) 2009-11-25 2013-08-06 Massachusetts Institute Of Technology Water desalination using directional solvent extraction
US20120318729A1 (en) 2009-12-03 2012-12-20 Yale University Office Of Cooperative Research High Flux Thin-Film Composite Forward Osmosis and Pressure-Retarded Osmosis Membranes
US8695343B2 (en) 2009-12-04 2014-04-15 General Electric Company Economical and sustainable disposal of zero liquid discharge salt byproduct
US20110155666A1 (en) 2009-12-30 2011-06-30 Chevron U.S.A. Inc. Method and system using hybrid forward osmosis-nanofiltration (h-fonf) employing polyvalent ions in a draw solution for treating produced water
US20130056193A1 (en) 2010-01-12 2013-03-07 Sylvan Source, Inc. Heat transfer interface
US20150083656A1 (en) 2010-01-14 2015-03-26 Bp Exploration Operating Company Limited Process of supplying water of controlled salinity
US20110180479A1 (en) 2010-01-27 2011-07-28 Milton Roy Company Zero liquid discharge water treatment system and method
US20110198285A1 (en) 2010-02-17 2011-08-18 Katana Energy Llc Zero Discharge Water Desalination Plant With Minerals Extraction Integrated With Natural Gas Combined Cycle Power Generation
US20110215039A1 (en) 2010-03-04 2011-09-08 Terragroup Corporation Lightweight modular water purification system with reconfigurable pump power options
US20100314238A1 (en) 2010-04-30 2010-12-16 Sunlight Photonics Inc. Hybrid solar desalination system
US20130118887A1 (en) 2010-04-30 2013-05-16 Sunlight Photonics Inc. Hybrid solar desalination system
US20130193074A1 (en) 2010-05-13 2013-08-01 Clean Teq Holdings Ltd. Water treatment process
US8679347B2 (en) 2010-05-26 2014-03-25 Riad A. Al-Samadi Multi-use high water recovery process
CN102258942A (en) 2010-05-26 2011-11-30 覃正元 Three-stage reverse osmosis
WO2011159743A1 (en) 2010-06-15 2011-12-22 General Electric Company Seawater desalination plant and production of high purity salt
CN102933507A (en) 2010-06-15 2013-02-13 通用电气公司 Seawater desalination plant and production of high purity salt
US20110303607A1 (en) 2010-06-15 2011-12-15 General Electric Company Seawater desalination plant and production of high purity salt
US20120012511A1 (en) 2010-07-14 2012-01-19 Korea Institute Of Machinery & Materials Apparatus for osmotic power generation and desalination using salinity difference
US20120012005A1 (en) 2010-07-16 2012-01-19 Solution Dynamics Regenerative Dryers With A Bypass
US20120037568A1 (en) 2010-08-10 2012-02-16 Siemens Industry, Inc. Controlled method of minimizing radioactive sludge generation in post stimulation flowback and/or produced water treatment from a saltwater, oil and/or gas well
US20120067820A1 (en) 2010-09-21 2012-03-22 Water Standard Company Llc Method and apparatus for dynamic, variable-pressure, customizable, membrane-based water treatment for use in improved hydrocarbon recovery operations
US9266762B2 (en) 2010-09-30 2016-02-23 General Electric Company Membrane filtration process with high water recovery
US20120145635A1 (en) 2010-10-14 2012-06-14 Lucas Iii Arthur L Treatment of waters with multiple contaminants
US20120090833A1 (en) 2010-10-15 2012-04-19 Shell Oil Company Water injection systems and methods
US20120125603A1 (en) 2010-11-19 2012-05-24 Willingham Thomas W Systems and Methods For Enhanced Waterfloods
US8999172B1 (en) 2010-12-16 2015-04-07 Global Water Advisors, Inc. Selective removal of dissolved substances from aqueous solutions
US20140008291A1 (en) 2011-01-25 2014-01-09 Nanyang Technological University Forward osmosis membrane and method of forming a forward osmosis membrane
US20120199524A1 (en) 2011-02-09 2012-08-09 Ccs Midstream Services, Llc. Method and apparatus for treating well flow-back and produced water or other wastewater
US8647477B2 (en) 2011-02-15 2014-02-11 Massachusetts Institute Of Technology High-efficiency thermal-energy-driven water purification system
US20120234765A1 (en) 2011-03-15 2012-09-20 Lehigh University Method of treatment of produced water and recovery of important divalent cations
US20120279396A1 (en) 2011-03-15 2012-11-08 Mks Instruments, Inc. System to remove Dissolved Gases Selectively from Liquids
US20140284929A1 (en) 2011-03-30 2014-09-25 Toray Industries, Inc. Concentration difference power generation device and method for operating same
CN103547798A (en) 2011-03-30 2014-01-29 东丽株式会社 Concentration difference power generation device and method for operating same
US20130092622A1 (en) 2011-04-01 2013-04-18 Millipore Corporation Nanofiber containing composite membrane structures
US20140021135A1 (en) 2011-04-06 2014-01-23 Liberty Hydro, Inc. Treatment of waters with multiple contaminants
WO2012138502A1 (en) 2011-04-06 2012-10-11 Ysawyer John E Treatment of waters with multiple contaminants
WO2012142396A1 (en) 2011-04-14 2012-10-18 Basf Se Method of dissolving and/or inhibiting the deposition of scale on a surface of a system
WO2012148911A2 (en) 2011-04-25 2012-11-01 Oasys Water, Inc. Osmotic separation systems and methods
US20120267307A1 (en) 2011-04-25 2012-10-25 Mcginnis Robert L Osmotic separation systems and methods
US20120292259A1 (en) 2011-05-17 2012-11-22 High Sierra Energy, LP System and method for treatment of produced waters containing gel
US8820723B1 (en) 2011-05-24 2014-09-02 Saltworks Technologies, Inc. Method, apparatus and system for concentrating solutions using evaporation
CA2821453C (en) 2011-05-24 2014-01-14 Saltworks Technologies Inc. Method, apparatus and system for concentrating solutions using evaporation
CA2816746C (en) 2011-05-24 2014-04-01 Saltworks Technologies Inc. Method, apparatus and system for concentrating solutions using evaporation
WO2012159203A1 (en) 2011-05-24 2012-11-29 Saltworks Technologies Inc. Method, apparatus and system for concentrating solutions using evaporation
US8857798B1 (en) 2011-05-24 2014-10-14 Saltworks Technologies Inc. Method, apparatus and system for concentrating solutions using evaporation
CA2821458C (en) 2011-05-24 2014-07-08 Saltworks Technologies Inc. Method, apparatus and system for concentrating solutions using evaporation
US8727325B2 (en) 2011-05-24 2014-05-20 Saltworks Technologies Inc. Method, apparatus and system for concentrating solutions using evaporation
US20120312755A1 (en) 2011-06-10 2012-12-13 Aqua-Pure Ventures Inc. Mobile clarifier and sludge dewatering system for onsite waste water treatment
CA2779732A1 (en) 2011-06-10 2012-12-10 Aqua-Pure Ventures Inc. Mobile clarifier and sludge dewatering system for onsite waste water treatment
US8197693B2 (en) 2011-07-03 2012-06-12 King Abdulazia City for Science and Technology (KACST) Apparatus and process for producing electricity using pressure retarded osmosis during desalination of sea water
US20120091061A1 (en) 2011-07-03 2012-04-19 King Abdulaziz City for Organization Name Science and Technology "KACST" Apparatus and process for desalination of brackish water using pressure retarded osmosis
US20130008079A1 (en) 2011-07-05 2013-01-10 Dr. Deborah Duen Ling Chung Coagulation of oil in water and the resulting floating semisolid complex
WO2013012548A1 (en) 2011-07-20 2013-01-24 Cameron International Corporation System to provide a supply of controlled salinity water for enhanced oil recovery
US20130043190A1 (en) 2011-08-17 2013-02-21 Riad A. Al-Samadi High Recovery Drinking Water Process
US20140263081A1 (en) 2011-09-09 2014-09-18 Sylvan Source,Inc. Industrial water purification and desalination
US8889000B2 (en) 2011-09-15 2014-11-18 Storm Drain Technologies, Llc Apparatus, methods, and system for treatment of stormwater and waste fluids
WO2013037047A1 (en) 2011-09-15 2013-03-21 Saltworks Technologies Inc. Method, apparatus and system for desalinating saltwater
US20140197029A1 (en) 2011-09-15 2014-07-17 Saltworks Technologies, Inc. Method, apparatus and system for desalinating saltwater
US8523985B2 (en) 2011-09-23 2013-09-03 Massachusetts Institute Of Technology Bubble-column vapor mixture condenser
US20130075940A1 (en) 2011-09-23 2013-03-28 King Fahd University Of Petroleum And Minerals Bubble-Column Vapor Mixture Condenser
US9072984B2 (en) 2011-09-23 2015-07-07 Massachusetts Institute Of Technology Bubble-column vapor mixture condenser
US20130074694A1 (en) 2011-09-23 2013-03-28 Massachusetts Institute Of Technology Bubble-Column Vapor Mixture Condenser
US8778065B2 (en) 2011-09-23 2014-07-15 Massachusetts Institute Of Technology Humidification-dehumidification system including a bubble-column vapor mixture condenser
US20130075098A1 (en) 2011-09-27 2013-03-28 Fluor Technologies Corporation Methods for treatment and use of produced water
US9428404B2 (en) 2011-10-04 2016-08-30 Massachusetts Institute Of Technology Water extraction using a directional solvent
US20130087501A1 (en) 2011-10-06 2013-04-11 General Electric Compay Seawater desalination process
US20130105323A1 (en) 2011-10-27 2013-05-02 David J. Averbeck Ion Removal Using a Capacitive Deionization System
CN102363101A (en) 2011-11-14 2012-02-29 天津森诺过滤技术有限公司 Submerged membrane filtration system and process for removing suspended solid from phosphating liquid
WO2013078124A1 (en) 2011-11-23 2013-05-30 Advanced Aqua Group Water conversion system
US20130213892A1 (en) 2011-12-22 2013-08-22 Water Standard Company (Mi) Method and control devices for production of consistent water quality from membrane-based water treatment for use in improved hydrocarbon recovery operations
KR20130074104A (en) 2011-12-26 2013-07-04 한국건설기술연구원 Combination-type desalination apparatus of forward osmosis(fo) and reverse osmosis(ro) using multi-water source as feed water and sea water as draw solution, and system and method for controlling membrane process for the same
US9085971B2 (en) 2011-12-29 2015-07-21 Shell Oil Company Method and system for enhancing oil recovery (EOR) by injecting treated water into an oil bearing formation
US20130186822A1 (en) 2012-01-20 2013-07-25 Hydration Systems, Llc Low energy forward osmosis membrane water processing system
US20130199921A1 (en) 2012-02-07 2013-08-08 Massachusetts Institute Of Technology Carrier-Gas Humidification-Dehumidification Using Heat-Transfer Members for Enhanced Heat Recovery
US20130233786A1 (en) 2012-02-22 2013-09-12 Richard Paul Posa System and method for treating water
US20130240442A1 (en) 2012-03-16 2013-09-19 Ravi Chidambaran Process for purification of produced water
US20130256228A1 (en) 2012-03-30 2013-10-03 Hydration Systems, Llc Use of novel draw solutes and combinations thereof to improve performance of a forward osmosis system and process
US20150060360A1 (en) 2012-04-12 2015-03-05 Dxv Water Technologies, Llc Systems and methods of membrane separation
WO2013158315A1 (en) 2012-04-18 2013-10-24 Hydration Systems, Llc Method for producing water for enhanced oil recovery
US8980100B2 (en) 2012-04-23 2015-03-17 Aquatech International Corporation Low energy reverse osmosis process
CA2818055C (en) 2012-04-25 2013-11-26 Saltworks Technologies Inc. Modular humidification-dehumidification apparatus for concentrating solutions
WO2013159220A1 (en) 2012-04-25 2013-10-31 Saltworks Technologies Inc. Modular humidification-dehumidification apparatus for concentrating solutions
WO2013172605A1 (en) 2012-05-15 2013-11-21 고려대학교 산학협력단 Low energy salt water desalination method and salt water desalination system using pressure retarded osmosis and reverse osmosis
US20140069821A1 (en) 2012-05-23 2014-03-13 High Sierra Energy, LP System and method for treatment of produced waters
US20130318743A1 (en) 2012-05-30 2013-12-05 GM Global Technology Operations LLC Check link assembly with adjustable detent feature
KR101229482B1 (en) 2012-07-12 2013-02-04 한국기계연구원 Apparatus and method for hybrid desalination
US8496234B1 (en) 2012-07-16 2013-07-30 Massachusetts Institute Of Technology Thermodynamic balancing of combined heat and mass exchange devices
US20140042058A1 (en) 2012-08-09 2014-02-13 Shell Oil Company Process for producing and separating oil
US20140041856A1 (en) 2012-08-09 2014-02-13 Shell Oil Company System for producing and separating oil
US20140042061A1 (en) 2012-08-13 2014-02-13 Enviro Water Minerals Company, Inc. Heating system for desalination
DE102012017860A1 (en) 2012-09-11 2014-05-15 Peter Vinz Treatment method for enriching on separating mixture components from sewage liquid mixtures, involves depressurizing and re-introducing permeate from primary channel of first treatment zone into secondary channel of second treatment zone
WO2014058696A1 (en) 2012-10-10 2014-04-17 M-I L.L.C. Boron removal system and method
US20140116956A1 (en) 2012-10-28 2014-05-01 SYNCRUDE CANADA LTD. in trust for the owners of the Syncrude Project Fort McMurray Co-processing of fluid fine tailings and fresh oil sands tailings
WO2014088826A1 (en) 2012-12-07 2014-06-12 Aquatech International Corporation Water treatment process
US20150353397A1 (en) 2013-01-10 2015-12-10 Tzahi Y. Cath Water reuse system and method
US20140197022A1 (en) 2013-01-15 2014-07-17 King Abdulaziz City For Science And Technology Solar-powered humidification-dehumidification desalination system
WO2014121153A2 (en) 2013-02-01 2014-08-07 Lake Country Fracwater Specialists, Llc Method and apparatus for treating natural gas and oil well waste waters for removal of contaminants and dissolved solids
US9950297B2 (en) 2013-02-06 2018-04-24 Korea Advanced Institute Of Science And Technology Method for concentrating aqueous containing solute into high concentration by hydraulic-membrane process under no difference in osmotic pressure
WO2014150848A1 (en) 2013-03-14 2014-09-25 Massachusetts Institute Of Technology Ion sequestration for scale prevention in high-recovery desalination systems
US9617179B2 (en) 2013-03-14 2017-04-11 Massachusetts Institute Of Technology Ion sequestration for scale prevention in high-recovery desalination systems
US20170174543A1 (en) 2013-03-14 2017-06-22 Massachusetts Institute Of Technology Ion Sequestration for Scale Prevention
US9957180B2 (en) 2013-03-14 2018-05-01 Massachusetts Institute Of Technology Ion sequestration for scale prevention
US20140263055A1 (en) 2013-03-14 2014-09-18 Massachusetts Institute Of Technology Ion Sequestration for Scale Prevention in High-Recovery Desalination Systems
US20200086274A1 (en) 2013-03-15 2020-03-19 Porifera, Inc. Advancements in osmotically driven membrane systems including multi-stage purification
WO2014144778A1 (en) 2013-03-15 2014-09-18 Porifera, Inc. Advancements in osmotically driven membrane systems including multi-stage purification
WO2014144704A1 (en) 2013-03-15 2014-09-18 Porifera, Inc. Advancements in osmotically driven membrane systems including low pressure control
WO2014162094A2 (en) 2013-04-03 2014-10-09 Total Sa Production of injection water by coupling direct‑osmosis methods with other methods of filtration
US20160040522A1 (en) 2013-04-03 2016-02-11 Total Sa Production of injection water by coupling direct-osmosis methods with other methods of filtration
US20140339162A1 (en) 2013-05-17 2014-11-20 Baker Hughes Incorporated Boron removal from oilfield water
WO2014188450A1 (en) 2013-05-23 2014-11-27 Council Of Scientific & Industrial Research Improved process to retain nutritious constituents in potable water obtained through desalination
US20140367871A1 (en) 2013-06-12 2014-12-18 King Fahd University Of Petroleum & Minerals Multi-Stage Bubble Column Humidifier
US9120033B2 (en) 2013-06-12 2015-09-01 Massachusetts Institute Of Technology Multi-stage bubble column humidifier
WO2014200829A1 (en) 2013-06-12 2014-12-18 Massachusetts Institute Of Technology Multi-stage bubble column humidifier
US20150013987A1 (en) 2013-07-11 2015-01-15 Baker Hughes Incorporated Method for reducing sulfide in oilfield waste water and making treated water
US20150014248A1 (en) 2013-07-15 2015-01-15 Hydration Systems, Llc Method and system for generating strong brines
US9969638B2 (en) 2013-08-05 2018-05-15 Gradiant Corporation Water treatment systems and associated methods
WO2015021062A1 (en) 2013-08-05 2015-02-12 Gradiant Corporation Water treatment systems and associated methods
US20150060286A1 (en) 2013-08-05 2015-03-05 Gradiant Corporation Water treatment systems and associated methods
US20150053619A1 (en) 2013-08-21 2015-02-26 Baker Hughes Incorporated Process for Hardness and Boron Removal
US9079117B2 (en) 2013-09-12 2015-07-14 Gradiant Corporation Systems including a condensing apparatus such as a bubble column condenser
WO2015038983A2 (en) 2013-09-12 2015-03-19 Gradiant Corporation Systems including a condensing apparatus such as a bubble column condenser
US9700811B2 (en) 2013-09-12 2017-07-11 Gradiant Corporation Systems including a condensing apparatus such as a bubble column condenser
US20150129410A1 (en) 2013-09-12 2015-05-14 Gradiant Corporation Systems including a condensing apparatus such as a bubble column condenser
WO2015042584A1 (en) 2013-09-23 2015-03-26 Gradiant Corporation Desalination systems and associated methods
US20150083577A1 (en) 2013-09-23 2015-03-26 Gradiant Corporation Desalination systems and associated methods
US20150107841A1 (en) 2013-10-23 2015-04-23 Shell Oil Company Process for reducing viscosity of polymer-containing fluid produced in the recovery of oil
WO2015061194A1 (en) 2013-10-23 2015-04-30 Shell Oil Company Process for recovery of oil from an oil-bearing formation
US20150107840A1 (en) 2013-10-23 2015-04-23 Shell Oil Company Process for recovery of oil from an oil-bearing formation
US20170044033A1 (en) 2014-04-23 2017-02-16 Massachusetts Institute Of Technology Method and Apparatus for Partially Desalinating Produced Water to Form Extraction Fluid Used for Fossil Fuel Extraction
US20170036171A1 (en) 2014-04-23 2017-02-09 Massachusetts Institute Of Technology Liquid Purification System
US20160001235A1 (en) 2014-07-07 2016-01-07 E I Du Pont De Nemours And Company Filtration membranes
WO2016057764A1 (en) 2014-10-10 2016-04-14 Oasys Water, Inc. Osmotic separation systems and methods
US9556041B2 (en) 2014-10-22 2017-01-31 Gradiant Corporation Selective scaling in desalination water treatment systems and associated methods
US9221694B1 (en) 2014-10-22 2015-12-29 Gradiant Corporation Selective scaling in desalination water treatment systems and associated methods
US20160137526A1 (en) 2014-10-22 2016-05-19 Gradiant Corporation Selective scaling in desalination water treatment systems and associated methods
US10258926B2 (en) 2015-02-11 2019-04-16 Massachusetts Institute Of Technology Hybridization of humidification-dehumidification and pressure-retarded osmosis
US20160229705A1 (en) 2015-02-11 2016-08-11 Gradiant Corporation Methods and systems for producing treated brines for desalination
US20160228795A1 (en) 2015-02-11 2016-08-11 Gradiant Corporation Methods and systems for producing treated brines
US20160244349A1 (en) 2015-02-11 2016-08-25 Gradiant Corporation Production of ultra-high-density brines
US20180036682A1 (en) 2015-03-05 2018-02-08 Surrey Aquatechnology Limited Purification of highly saline feeds
US20160339357A1 (en) 2015-05-21 2016-11-24 Gradiant Corporation Systems including an apparatus comprising both a humidification region and a dehumidification region with heat recovery and/or intermediate injection
US20160339354A1 (en) 2015-05-21 2016-11-24 Gradiant Corporation Transiently-operated desalination systems and associated methods
US9266748B1 (en) 2015-05-21 2016-02-23 Gradiant Corporation Transiently-operated desalination systems with heat recovery and associated methods
US20160339356A1 (en) 2015-05-21 2016-11-24 Gradiant Corporation Systems including an apparatus comprising both a humidification region and a dehumidification region
US9206060B1 (en) 2015-05-22 2015-12-08 Basel Abusharkh Method for purifying liquids
US20160339390A1 (en) 2015-05-22 2016-11-24 Basel Abusharkh Method of solvent recovery from a dilute solution
US9427705B1 (en) 2015-05-22 2016-08-30 Basel Abusharkh Method of solvent recovery from a dilute solution
US10953367B2 (en) 2015-07-24 2021-03-23 Lab to Market Inc. Method of osmotic pressure free reverse osmosis for enriching solute-containing solution to high concentration
WO2017019944A1 (en) 2015-07-29 2017-02-02 Gradiant Corporation Osmotic desalination methods and associated systems
US10518221B2 (en) 2015-07-29 2019-12-31 Gradiant Corporation Osmotic desalination methods and associated systems
WO2017030932A1 (en) 2015-08-14 2017-02-23 Gradiant Corporation Selective retention of multivalent ions
WO2017030941A1 (en) 2015-08-14 2017-02-23 Gradiant Corporation Production of multivalent ion-rich streams using humidification-dehumidification systems
WO2017030937A1 (en) 2015-08-14 2017-02-23 Gradiant Corporation Production of multivalent ion-rich process streams using multi-stage osmotic separation
US20180236372A1 (en) 2015-08-14 2018-08-23 Gradiant Corporation Production of multivalent ion-rich streams using humidification-dehumidification systems
US20180236406A1 (en) 2015-08-14 2018-08-23 Gradiant Corporation Production of multivalent ion-rich process streams using multi-stage osmotic separation
US20180244545A1 (en) 2015-08-14 2018-08-30 Gradiant Corporation Selective retention of multivalent ions
US10245555B2 (en) 2015-08-14 2019-04-02 Gradiant Corporation Production of multivalent ion-rich process streams using multi-stage osmotic separation
WO2017044645A1 (en) 2015-09-08 2017-03-16 Gradiant Corporation Systems and methods for treatment of water, such as oilfield wastewater, via chemical coagulation
WO2017044668A1 (en) 2015-09-08 2017-03-16 Gradiant Corporation Systems and methods for removal of boron from water, such as oilfield wastewater
US20170144906A1 (en) 2015-09-08 2017-05-25 Gradiant Corporation Systems and methods for treatment of water, such as oilfield wastewater, via chemical coagulation
WO2017127607A1 (en) 2016-01-22 2017-07-27 Gradiant Corporation Formation of solid salts using high gas flow velocities in humidifiers, such as multi-stage bubble column humidifiers
WO2017147113A1 (en) 2016-02-22 2017-08-31 Gradiant Corporation Hybrid desalination systems and associated methods
JP2018001111A (en) 2016-07-05 2018-01-11 東洋紡株式会社 Processing method of desalinating salt water and processing system of desalinating salt water
US20180008919A1 (en) 2016-07-06 2018-01-11 Gradiant Corporation Solids handling in water treatment systems and associated methods
WO2018075637A1 (en) 2016-10-19 2018-04-26 Gradiant Corporation Osmotic membrane
US20180104649A1 (en) 2016-10-19 2018-04-19 Gradiant Corporation Osmotic Membrane
WO2018084246A1 (en) 2016-11-02 2018-05-11 東洋紡株式会社 Concentration method and concentration device
US20190224624A1 (en) 2017-02-15 2019-07-25 Hitachi, Ltd. Reverse osmosis treatment apparatus and reverse osmosis treatment method
WO2019097261A1 (en) 2017-11-20 2019-05-23 Surrey Aquatechnology Limited Solvent separation
US10308524B1 (en) 2019-01-15 2019-06-04 Kuwait Institute For Scientific Research Pressure-reduced saline water treatment system
US10940439B1 (en) 2019-12-10 2021-03-09 Kuwait Institute For Scientific Research High water recovery hybrid membrane system for desalination and brine concentration

Non-Patent Citations (63)

* Cited by examiner, † Cited by third party
Title
[No Author Listed], 13.5 Colligative Properties. Prentice Hall. Accessed Jul. 9, 2019 as available Aug. 23, 2012 from <https://web.archive.org/web/20120823004120/http://wps.prenhall.com/wps/media/objects/3082/3156628/blb1305.htmll>. 10 pages.
[No Author Listed], Accepta 4360 Material Safety Data Sheet. Accepta Ltd. Manchester, UK. Jul. 19, 2011. 5 pages.
[No Author Listed], Caustic Soda 50% Material Safety Data Sheet. Univar. Redmond, Washington. Apr. 8, 2013. 10 pages.
[No Author Listed], Color Removal Using Ozone. Spartan Environmental Technologies Air and Water Treatment—Technical Bulletin. Available Jul. 21, 2006. Last accessed Mar. 2, 2017 from <http://www.spartanwatertreatment.com/ozone-color-removal.html>. 2 pages.
[No Author Listed], Everything you want to know about Coagulation & Flocculation. Chapter 1: The Electrokinetic Connection. Zeta-Meter, Inc. Staunton, VA. 4th Edition. 1993:1-8.
[No Author Listed], F0 Plant Completes 1-Year of Operation. Water Desalination Report Nov. 15, 2010:2 pages.
[No Author Listed], Forward Osmosis. Wikipedia. Accessed Jul. 9, 2019 as available May 5, 2007 from <https://web.archive.org/web/20080317095053/https://en.wikipedia.org/wiki/Forward_osmosis>. 3 pages.
[No Author Listed], Hi-Cal Hydrate Material Safety Data Sheet. Chemical Lime Co. Fort Worth, Texas. May 1, 2008. 6 pages.
[No Author Listed], Landfill Leachate Treatment. Osmotek, Inc. Corvallis, OR. Accessed Jul. 9, 2019 as available Oct. 9, 2007 from <https://web.archive.org/web/20071009130111/http://www.rimnetics.com/OSMOTEK%20BROCHURE.pdf>. 7 pages.
[No Author Listed], Polyaluminum Chloride Solution Material Safety Data Sheet. GEO Specialty Chemicals, Ltd. Little Rock, Arkansas. Mar. 12, 2015. 11 pages.
[No Author Listed], Servco 1010 Material Safety Data Sheet. Servco Chemicals. Lubbock, Texas. Aug. 7, 2013. 4 pages.
[No Author Listed], Soda Ash Material Safety Data Sheet. Univar. Redmond, Washington. Apr. 7, 2003. 10 pages.
Achilli et al., Selection of inorganic-based draw solutions for forward osmosis applications. Journal of Membrane Science. 2010;364:233-41. Epub Aug. 14, 2010.
Akram et al., Energy Utilization of Brine from an MSF Desalination Plant by Pressure Retarded Osmosis. The International Desalination Association World Congress on Desalination and Water Reuse. Tianjin, China. Oct. 2013. 12 pages.
Al-Hallaj et al., Solar desalination with a humidification-dehumidification cycle: performance of the unit. Desalination. 1998;120:273-80.
Alshakhs, Modifying Water Salinity to Improve Oil Recovery. Stanford Academic Report. Oct. 29, 2013. Last accessed on Dec. 8, 2016 at <http://large.stanford.edu/courses/2013/ph240/alshakhsl/>. 2 pages.
Aramco, Saudi Aramco's ‘Smart Water’ May Aid Oil Production. Rigzone. Jul. 29, 2009. <http://www.rigzone.com/news/article_pf.asp?a_id=78707> Last accessed Jul. 30, 2015. 1 page.
Arthur et al., Technical Summary of Oil & Gas Produced Water Treatment Technologies. All Consulting, LLC (Mar. 2005). Last accessed on Dec. 21, 2016 from <http://dvikan.no/ntnu-studentserver/reports/ALLConsulting-WaterTreatmentOptionsReport.pdf>. 53 pages.
Banchik et al., Thermodynamic Analysis of a Reverse Osmosis Desalination System Using Forward Osmosis for Energy Recovery. Proceedings of the ASME 2012 International Mechanical Engineering Congress & Exposition. American Society of Mechanical Engineers. Houston, Texas. Nov. 9-15, 2012. 13 pages.
Beasley et al., Analysis of a pressure driven absorption refrigeration cycle. International Journal of Energy Research. Jan./Mar. 1988;12(1):175-84.
Bruno, A Low-Energy Water Purifier. MIT Technology Review. Jan. 8, 2009:4 pages.
Burk, New Technology Spotlight. CaribDA News. 2012 Fall;2(4):6-7.
Cath et al., A Novel Hybrid Forward Osmosis Process for Drinking Water Augmentation Using Impaired Water and Saline Water Sources. WERC and Water Research Foundation. 2009:84 pages.
Cath et al., Forward osmosis: Principles, applications, and recent developments. Journal of Membrane Science. Sep. 15, 2006;281(1-2):70-87.
Chung et al., Forward osmosis processes: Yesterday, today and tomorrow. Desalination. 2012;287:78-81. Epub Jan. 11, 2011.
El-Dessouky et al., Multiple-effect evaporation desalination systems: thermal analysis. Desalination. 1999;125:259-76.
Extended European Search Report for EP App. No. 16831402.9 dated Mar. 25, 2019.
Ge et al., Exploration of polyelectrolytes as draw solutes in forward osmosis processes. Water Research. 2012;46:1318-26. Epub Dec. 27, 2011.
Global Water Intelligence, Water Desalination Report. Tom Pankratz, ed. Dec. 17, 2012;48(48):1-4.
Govindan, Thermal Design of Humidification Dehumidification Systems for Affordable and Small-scale Desalination. Doctoral Thesis. Massachusetts Institute of Technology. Sep. 2012. 286 pages.
Gude, Energy consumption and recovery in reverse osmosis. Desalination and Water Treatment. 2011;36(1-3):239-60.
Huang et al., The bridging force between colloidal particles in a polyelectrolyte solution. Langmuir. Nov. 27, 2012;28(47):16300-5. doi:10.1021/1a303918p.
International Preliminary Report on Patentability dated Feb. 8, 2018 for PCT/US16/44663.
International Search Report and Written Opinion dated Oct. 14, 2016 for PCT/US16/44663.
Khayet et al., Determination of surface and bulk pore sizes of flat-sheet and hollow-fiber membranes by atomic force microscopy, gas permeation and solute transport methods. Desalination. 2003;158:57-64.
Kim et al., Effect of PEG additive on membrane formation by phase inversion. Journal of Membrane Science. 1998;138:153-63.
Klausner et al., Evaporative heat and mass transfer for the diffusion driven desalination process. Heat Mass Transfer. 2006;42:528-36.
Kwak et al., New Insights on the Role of Multivalent Ions In Water-Carbonate Rock Interactions. Saudi Journal of Technology. 2014:25-38. Last accessed on Dec. 8, 2016 at <http://www.saudiaramco.com/content/dam/Publications/Journal-of-Technology/Summer2014/New_Insights.pdf>.
Li, Experimental Analysis of Produced Water Desalination by a Humidification-Dehumidification Process. 2009. 62 pages.
Li, Mineral precipitation and deposition in cooling systems using impaired waters: mechanisms, kinetics, and inhibition. Dissertation defended Jul. 27, 2010. 224 pages.
Ma, Yaopin GMP Chejian Shixun Jiaocheng. China Medical Science Press. Jun. 2016;1:3 pages.
McCutcheon et al., Influence of concentrative and dilutive internal concentration polarization on flux behavior in forward osmosis. Journal of Membrane Science. Nov. 2006;284(1-2):237-47.
McGinnis et al., Pilot demonstration of the NH3/CO2 forward osmosis desalination process on high salinity brines. Desalination. Mar. 2013;312:67-74. Supporting information included.
Miller et al., Forward Osmosis: A New Approach to Water Purification and Desalination. Sandia National Laboratories. Albuquerque, NM. Jul. 2006:51 pages.
Moghadasi et al., Scale deposits in porous media and their removal by EDTA injection. ECI Symposium Series. 2007. vol. RP5. Article 10. p. 57-70.
Narayan et al., The potential of solar-driven humidification-dehumidification desalination for small-scale decentralized water production. Renewable and Sustainable Energy Reviews. 2010;14:1187-1201.
Narayan et al., Thermal design of the humidification desalination system: an experimental investigation. International Journal of Heat and Mass Transfer. 2013;58:1-9.
Narayan et al., Thermodynamic balancing of the humidification dehumidification desalination system by mass extraction and injection. International Journal of Heat and Mass Transfer. 2013;57:756-70.
Office Action for AU Application No. 2016298326 dated Aug. 6, 2021.
Office Action for CA Application No. 2,993,007 dated Apr. 22, 2022.
Office Action for CN Application No. 201680057000.2 dated Oct. 29, 2021.
Office Action for SA Application No. 518390827 dated Apr. 7, 2022.
Office Action for SA Application No. 518390827 dated Sep. 12, 2021.
Office Communication for CN Application No. 201680057000.2 dated Mar. 29, 2021.
Office Communication for CN Application No. 201680057000.2 dated May 29, 2020.
Office Communication for IN Application No. 201817005629 dated Aug. 18, 2021.
Office Communication for Indian Patent Application No. 201817005629 dated Feb. 25, 2020.
Riffat et al., Analysis of using centrifugal reverse osmosis in absorption refrigeration systems. Chartered Institute of Building Services Engineers. 2001 Conference. 5 pages.
Sahin, A Mathematical Model for Explanation of Ion Exchange of the Boric Acid Adsorption. Jour. Chem. Soc. Pak. 1998;20(1):12-8.
SINEX, EDTA—A molecule with a complex story. University of Bristol, School of Chemistry. <www.chm.bris.ac.uk/motm/edta/edtah.htm> (accessed Jan. 8, 2013). Aug. 1, 2007.
Thiel et al., Hybridization of Humidification-Dehumidification and Pressure Retarded Osmosis for Brine Concentration Applications. The International Desalination Association World Congress on Desalination and Water Reuse. San Diego, California. Aug.-Sep. 2015. 8 pages.
Tiraferri et al., Relating performance of thin-film composite forward osmosis membranes to support layer formation and structure. Journal of Membrane Science. Nov. 12, 2010;367:340-52.
Zamen et al., Improvement of solar humidification-dehumidification desalination using multi-stage process. 6 pages. Accessed Jun. 6, 2014.

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